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Institut für Landtechnik
Professur für Haushalts- und Verfahrenstechnik
Prof. Dr. rer. nat. Rainer Stamminger
Sustainable use of washing machine: modeling the consumer
behavior related resources consumption in use of washing
machines
I n a u g u r a l – D i s s e r t a t i o n
zur
Erlangung des Grades
Doktor der Ernährungs- und Haushaltswissenschaft
(Dr. oec. troph.)
der
Landwirtschaftlichen Fakultät
der
Rheinischen Friedrich-Wilhelms-Universität Bonn
vorgelegt am 27.02.2014
von
Dipl. oec. troph. Emir Lasic
aus
Sanski Most, Bosnien und Herzegowina
Referent: Prof. Dr. rer. nat. Rainer Stamminger
Korreferent: Prof. Dr. Michael-Burkhard Piorkowsky
Tag der mündlichen Prüfung: 25. 04. 2014
Erscheinungsjahr: 2014
Abstract
Sustainable use of washing machine: modeling the consumer behavior related
resources consumption in use of washing machines
Two opposing trends are observed in Europe: an increase in the washing machines’
rated capacity and a decrease of the household size (hence a decrease of laundry that
has to be washed). The question poses: what kind of behavior is necessary to use the
washing machines with a higher rated capacity in a more sustainable manner? To
answer this question, a model of a washing machine (virtual washing machine) that is
based on real data of real-life washing machines is constructed. Furthermore, a model
that reproduces, to some extent, the household’s washing behavior (virtual washing
household) is developed.
By conducting parallel simulations of the usage of the virtual washing machine by the
virtual washing households and by varying device-, household- and behavioral
parameters, an optimal parameter combination with the lowest environmental impact
is determined.
The basis for the virtual washing machine is the data gained by testing nine washing
machines of different rated capacity (5 kg, 6 kg, 7 kg, 8 kg and 11 kg). All tests are
conducted in accordance with EN60456:2005, with some modifications regarding the
washing temperatures, load size and detergent dosage.
The predicting power of the virtual washing machine can be considered as good, given
that there are numerous differences in tested washing machines.
The virtual washing household is designed in such a manner that a washing cycle is
conducted when the household has enough laundry collected, so that the rated capacity
of the washing machine can be used. It also offers a possibility to conduct an
“emergency washing cycle” when the time needed for accumulating enough laundry
(to use rated capacity of the washing machine) exceeds the waiting time acceptable by
the consumer (so-called “maximal laundry waiting time”). This model offers a large
range of possibilities to simulate some of the consumer’s behavioral patterns.
With the moderating variable “maximal laundry waiting time”, it is possible to add a
time dimension to the virtual consumer model and thus explore the effects that might
occur when the consumer is ready to postpone an action (in this case the washing of
laundry) to a later point of time. The results show that a sustainable use of washing
machines with a higher rated capacity is possible when consumer behavior changes
towards waiting until enough laundry is accumulated, so that the rated capacity of the
washing machine is used.
Zusammenfassung
Nachhaltige Nutzung einer Waschmaschine: Modellieren des
verhaltensabhängigen Ressourcenverbrauchs bei der Waschmaschinennutzung
Zurzeit sind zwei Trends in Europa zu verzeichnen: einerseits erhöht sich die Anzahl
der Waschmaschinen mit einer höheren Nennfüllmenge und anderseits verringert sich
die Größe der Haushalte und somit der Wäscheanfall. Es stellt sich nun die Frage:
„Wie kann ein Haushalt mit einer kleinen Personenanzahl eine Waschmaschine mit
einer höheren Nennfüllmenge dennoch nachhaltig nutzen?“
Um diese Frage beantworten zu können, wird in dieser Arbeit zunächst, auf Basis von
Daten handelsüblicher Waschmaschinen, ein mathematisches Modell einer
Waschmaschine entwickelt (virtuelle Waschmaschine). Des Weiteren wird ein Modell
eines Haushaltes entwickelt, welches bis zu einem gewissen Grad das Waschverhalten
des Haushaltes nachahmt (virtueller Waschhaushalt).
Mittels paralleler Simulationen der Nutzung der virtuellen Waschmaschinen durch den
virtuellen Waschhaushalt und Veränderung der Geräte-, Haushalts- und
Verhaltensparameter werden geeignete Parameter-Kombinationen gesucht, bei
welchen die Auswirkungen auf die Umwelt am niedrigsten sind.
Die Basis für die virtuelle Waschmaschine bilden Daten aus Waschmaschinentests mit
9 Waschmaschinen verschiedener Nennfüllmengen (5 kg, 6 kg, 7 kg, 8 kg und 11 kg).
Alle Tests werden in Anlehnung an die EN60456:2005 durchgeführt, wobei
Waschtemperatur, Beladungsmenge und Waschmittelmenge modifiziert werden.
Trotz der Vielfalt der Waschmaschinen und den Unterschieden zwischen diesen, kann
die Vorhersagekraft der virtuellen Waschmaschine als gut bewertet werden.
Der virtuelle Waschhaushalt ist so gestaltet, dass ein Waschgang erst dann durchführt
wird, wenn genug Wäsche vorhanden ist, um die Nennfüllmenge der Waschmaschine
komplett auszunutzen. Des Weiteren bietet das Modell die Möglichkeit, einen
sogenannten „Notwaschgang“ durchzuführen. Dieser findet dann statt, wenn die Zeit,
welche nötig ist um genug Wäsche zu sammeln, die vom Verbraucher akzeptierte
Wartezeit (sogenannte „Maximale Wäschewartezeit“) überschreitet.
Dieses Modell ermöglicht die Simulation vieler verbrauchertypischer
Verhaltensmuster.
Mit der moderierenden Variablen „Maximale Wäschewartezeit“ ist es möglich, die
zeitliche Komponente in das Verbraucher-Modell einzubeziehen. Dadurch können
mögliche Effekte aufgezeigt werden, wenn der Verbraucher bereit ist, eine Handlung
(in diesem Fall Wäschewaschen) auf einen späteren Zeitpunkt zu verschieben.
Die Ergebnisse zeigen, dass eine nachhaltige Nutzung der Waschmaschine mit einer
höheren Nennfüllmenge dann möglich ist, wenn der Verbraucher das eigene Verhalten
dahin gehend verändert, dass er wartet, bis sich genug Wäsche angesammelt hat und
so die Nennfüllmenge der Waschmaschine ausgenutzt werden kann.
Content
Abstract
Zusammenfassung
1 Introduction ........................................................................................................... 1
1.1 Washing process ................................................................................................ 1
1.1.1 Mechanics ................................................................................................... 2
1.1.2 Temperature ................................................................................................ 3
1.1.3 Washing time .............................................................................................. 3
1.1.4 Chemistry .................................................................................................... 4
1.2 Washing machines ............................................................................................ 4
1.2.1 Horizontal axis washing machine ............................................................... 5
1.2.2 Vertical axis washing machine ................................................................... 6
1.2.2.1 Impeller (pulsator) type washing machine .......................................... 6
1.2.2.2 Agitator type washing machine ........................................................... 6
1.2.3 Washing machine markets and trends ........................................................ 6
1.2.4 Resource consumption for washing purposes ............................................ 7
1.2.4.1 Electricity consumption ....................................................................... 7
1.2.4.2 Water consumption .............................................................................. 8
1.2.5 Consumer behavior in use of washing machines ....................................... 9
1.2.5.1 Washing frequency ............................................................................ 10
1.2.5.2 Loading of the washing machine ....................................................... 11
1.2.5.3 Use of washing temperature and program ......................................... 12
1.3 Sustainability ................................................................................................... 12
1.4 Demographic trends........................................................................................ 13
1.5 Modeling approaches ...................................................................................... 14
2 Objective .............................................................................................................. 17
3 Material and methods ......................................................................................... 19
3.1 Material ............................................................................................................ 19
3.1.1 Tested washing machines ......................................................................... 19
3.1.2 Washing machine used for standardization and neutralization ................ 19
3.1.3 Test load ................................................................................................... 20
3.1.4 Detergent .................................................................................................. 20
3.1.5 Software .................................................................................................... 21
3.2 Methods ............................................................................................................ 21
3.2.1 Washing machines tests ............................................................................ 21
3.2.1.1 Load ................................................................................................... 21
3.2.1.2 Detergent dosing ................................................................................ 22
3.2.1.3 Temperature/program ........................................................................ 22
3.2.1.4 Normalization and conditioning ........................................................ 23
3.2.1.5 Reproduction tests .............................................................................. 24
3.2.1.6 Evaluation of the soil strips ............................................................... 24
3.2.1.7 Calculation the washing performance index ...................................... 24
3.2.1.8 Testing conditions .............................................................................. 25
3.2.2 Construction of the model of a virtual washing machine ......................... 25
3.2.2.1 Calculations of the consumption in CO2 equivalents ........................ 26
3.2.3 Construction of the model of virtual washing household ......................... 28
3.2.4 Combination of virtual washing household and virtual washing machine30
3.2.4.1 Correction of the detergent amount ................................................... 31
3.2.4.2 Scenario used for simulation ............................................................. 31
3.2.5 Average values calculations ..................................................................... 32
4 Results .................................................................................................................. 33
4.1 Results of the washing machines tests ........................................................... 33
4.1.1 Water consumption ................................................................................... 33
4.1.2 Energy consumption ................................................................................. 36
4.1.3 Washing performance ............................................................................... 37
4.1.4 Duration of the main wash........................................................................ 39
4.1.5 Washing temperature: nominal versus actual washing temperature ........ 40
4.2 Construction of model of virtual washing machine ..................................... 41
4.2.1 Water consumption equation .................................................................... 41
4.2.2 Energy consumption equation .................................................................. 43
4.2.3 Detergent consumption equation .............................................................. 45
4.3 Results of the virtual washing household modeling approach ................... 47
4.4 Results of yearly simulations ......................................................................... 50
4.4.1 Washing machine’s rated capacity versus household size ....................... 50
4.4.2 CO2 equivalent emission of water detergent and energy .......................... 55
4.4.3 Comparison of the time exposure ............................................................. 56
4.4.4 Comparison of average washing temperatures ......................................... 57
5 Discussion ............................................................................................................. 59
5.1 Virtual washing machine ................................................................................ 59
5.1.1 Equation for calculation of water consumption........................................ 59
5.1.2 Total water consumption .......................................................................... 61
5.1.3 Detergent consumption ............................................................................. 64
5.2 Virtual washing household ............................................................................. 66
5.3 Simulations ...................................................................................................... 67
5.3.1 Washing machine’s rated capacity ........................................................... 68
5.3.2 Resource consumption .............................................................................. 69
5.3.3 Washing frequency ................................................................................... 70
5.3.4 Average washing temperature .................................................................. 71
5.4 Deficits of the presented research .................................................................. 73
6 Conclusion ........................................................................................................... 75
7 Future prospects .................................................................................................. 77
8 References ............................................................................................................ 79
9 Abbreviations ...................................................................................................... 85
10 List of figures ....................................................................................................... 87
11 List of tables ......................................................................................................... 91
12 Apendix ................................................................................................................... I
12.1 Washing machine tests data .............................................................................. I
12.2 Virtual washing machine MATLAB source code ........................................ XI
12.3 Virtual washing household MATLAB source code .................................. XIII
Acknowledgements
INTRODUCTION 1
1 Introduction
Laundry washing, in the sense of cleaning textiles in aqueous liquor, is a complex
process involving the cooperative interaction of numerous physical and chemical
influences. In the broadest sense, washing can be defined as both removal by water or
by an aqueous detergent solution of poorly soluble residues, as well as the dissolution
of water-soluble impurities. (JAKOBI and LÖHR, 1987, SMULDERS et al., 2007)
TERPSTRA defines the primary objective of cleaning as “…restoration of the fitness for
use and the esthetical properties of the textiles, e.g. removal of soil, stains, odors and
creases and regaining surface smoothness and thermal isolation.”
(TERPSTRA, 2001, p.4) LEMARE defines other benefits from laundering processes, such
as the maintenance of the appropriate hygiene (LEMARE, 1987).
1.1 Washing process
The washing process is described as a function of different: washing temperatures,
length of washing cycles, types and amounts of detergent and applied mechanical
works. It is best described by using a circle, which many researchers today refer to as
Sinner’s Circle (Figure 1-1). (SINNER, 1960) STAMMINGER adds a further fifth parameter,
water (inner circle), which represents the combining element of all factors
(STAMMINGER, 2013).
Figure 1-1: Sinner’s circle (own representation)
Temperature
Chemistry Time
Water
Mechanics
INTRODUCTION 2
Each of these four factors can be substituted to a certain degree by the other three
factors and the resulting washing performance remains the same. For example, a
decrease of the temperature can be partially compensated by increasing either one or
more of the other factors, i.e. chemistry, washing time or mechanical agitation.
(WAGNER, 2011, KUTSCH et al., 1997, SMULDERS, 2007)
The combination of different factors depends on the washing technique employed. In
the case of washing laundry by hand, the portion of the mechanics is much higher than
the portion of the washing time (Figure 1-2). Laundry washing in a washing machine
at a higher temperature results in a higher contribution of the temperature in the
washing process (Figure 1-3).
Figure 1-2: Sinner's circle for washing by hand (own representation)
Figure 1-3: Sinner's circle for washing in a washing machine at a high temperature (own
representation)
1.1.1 Mechanics
In the washing process, the textiles are mixed with the wash liquor. The total amount
of wash liquor required in the main wash process is made up of two portions: liquor
soaked by the laundry (bound wash liquor) and liquor that remains free in the drum
(free wash liquor). (SMULDERS et al., 2007) In the case of manual laundering, the
mechanical action is done by rubbing and beating, stretching and squeezing of the
textiles. Sometimes this is done by using auxiliary devices. (SMULDERS et al., 2007)
In washing machines, the mechanical work is determined by: diameter of the drum,
reverse rhythm, water level, number of revolutions of the drum, position and number
Chem.
Temp. Mech.
Time Water
Chem.
Temp.
Mech.
Time
Water
INTRODUCTION 3
of the paddles in the drum, the amount of load, and the duration of the wash cycle.
(HLOCH et al., 1989)
The extent of the mechanical action imparted to the laundry can be altered by changing
the ratio of dry laundry weight to the volume of wash liquor (laundry-liquor-ratio). A
low wash liquor level and relatively rapid reversal causes a large mechanical effect on
the laundry. In contrast, a high wash liquor and slower reversal provides less
mechanical action. (SMULDERS et al., 2007)
1.1.2 Temperature
With an increase of the temperature, the soil removal normally increases. The elevated
temperature enhances the chemical reactions, solubilizes greasy soils and weakens the
binding forces of the soil on the fabric. (SMULDERS et al., 2007)
The maximal washing temperature is determined by the properties of the wash load.
With an increase of the temperature, the soil-binding capacity of the wash liquor
decreases, so that an extensive soil redisposition can be anticipated. Furthermore, with
an increase of the temperature, the knitting of the synthetic fibers increases as well.
In order to prevent those opposing trends in the praxis, the laundry washing process is
divided into different sub-processes. Today, normally the laundry washing is divided
into prewash and main wash, which is followed by the rinsing cycle. (HLOCH et al.,
1989)
1.1.3 Washing time
In order to remove the dirt from the textiles, the washing factors of chemistry and
mechanics have to interact together with the load at a certain washing temperature for
a certain period of time (WAGNER, 2011).
The duration of the washing process determines how long the detergent is allowed to
act. Longer cleaning times will increase the soil removal and thus improve the
cleaning performance (VAUGHN et al., 1941).
INTRODUCTION 4
At the beginning of the washing process, it is necessary to heat up the cold inlet water.
Heat-up time is the time required to achieve the preset temperature. Heat-up time
depends on the amount of laundry and hence the water quantity, the temperature of the
inlet water and the heating capacity of the washing machine. This heat-up time is
followed by the main washing time. (KUTSCH et al., 1997, SMULDERS, 2007, WAGNER,
2011)
1.1.4 Chemistry
The factor chemistry is accompanied with the medium water. A quantifying of this
factor in the form of a single operand is not possible since the washing chemistry does
not only depend on the very complex coaction of different detergent components, but
also depends on other factors, such as temperature or soil composition. (HLOCH et al.,
1989)
Besides the actual removal of soil, further functions of the chemical substances are:
water softening, emulation of lipid component, dispersion and stabilization of
particulate soil, bleaching of stains and dissolving of proteins. (KUTSCH et al., 1997)
The washing performance normally increases as the detergent concentration increases.
When the detergent concentration is too high, the washing performance decreases,
because a high foam production leads to a decrease of the mechanical force.
(HLOCH et al., 1989)
1.2 Washing machines
Washing machines that are presently used globally in domestic laundry care can be
divided mainly into two categories depending on the orientation of their axis:
horizontal and vertical axis washing machines. Following are the different types of
those automatic-washing systems. (KUTSCH et al., 1997)
INTRODUCTION 5
1.2.1 Horizontal axis washing machine
This type of washing machine consists of a stainless steel, perforated drum into which
the laundry is loaded, and an outer surrounding tub into which the water is filled. The
mechanical agitation of the laundry is done by rotating the drum around a horizontal
axis. Paddles, which are mounted on its inside, lift the laundry to the top and then let it
tumble down. (WAGNER, 2011; KUTSCH et al., 1997; SMULDERS, 2007)
Because the wash action does not require the clothing to be fully suspended in water,
only enough water is needed in order to moisten the fabric and to ensure a sufficient
transfer of suds between the water-soaked laundry and the free water. An electric
heater element on the bottom of the drum allows the heat-up of the water in the main
wash phase to the preset washing temperature, mainly between 30 °C and 60 °C.
(WAGNER, 2011; KUTSCH et al., 1997; SMULDERS, 2007)
Today’s state of the art domestic washing machines have many features built in, such
as a large number of different programs for all kind of textiles, automatic detection of
amount and type of textile, automatic dosing, steam generator for laundry refreshing
purposes, etc. (WAGNER, 2011; KUTSCH et al., 1997; SMULDERS, 2007)
Furthermore, modern washing machines frequently use the so-called fuzzy logic
control which governs partial processes of the washing program. Such a control is able
to automatically provide, for example, variable speeds of reversion of the drum
depending on the amount of foam produced during the wash cycle, or to control the
quantity of water intake and washing time depending on weight and type of wash load.
All those features should help the consumer to treat the laundry optimally.
(SMULDERS et al., 2007)
The horizontal axis type of washing machine is mainly used in Europe and Near East
countries. In recent years, this type of machine has also been gaining market shares in
all other regions as well. (WAGNER, 2011; KUTSCH et al., 1997; SMULDERS, 2007)
INTRODUCTION 6
1.2.2 Vertical axis washing machine
This type of washing machine uses a vertically mounted perforated drum that is itself
contained within a watertight tub. The laundry is freely suspended in the water. The
mechanical work is performed by moving the laundry in the water. Depending on its
laundry motion configuration, these washing machine can be subcategorized into:
1.2.2.1 Impeller (pulsator) type washing machine
In this type of machine, an impeller located on the bottom of the washing machine
induces a vortex. The vortex causes the laundry to circulate up and down in the water.
This type of washing machine is common in Japan, China and South Korea. These
machines normally do not contain a heating element, but use cold (or otherwise
preheated) water from the tap. (WAGNER, 2011; KUTSCH et al., 1997; SMULDERS, 2007)
1.2.2.2 Agitator type washing machine
In this type of washing machine, the mechanical work is produced by a device
(agitator) located in the center of the drum, which then rotates around its vertical axis
to the right and left. These machines normally are connected to an external hot and
cold water supply and mix these waters accordingly. This type of washing machine is
common in the USA and Canada. (WAGNER, 2011; KUTSCH et al., 1997; SMULDERS,
2007)
1.2.3 Washing machine markets and trends
The EU-27 washing machine stock in the residential sector was estimated to be around
172,85 million units (Bertoldi and Atanasiu, 2007). According to data presented in the
Preparatory Study for Eco-design Requirements of Energy-using Products (EuP) the
penetration of the washing machines on the European market is high: Germany
(96 %), Czech Republic (94,9 %), Poland (86 %), 87, France (94,7 %), Hungary
INTRODUCTION 7
(88 %), Spain (98,5 %), UK (94 %) Finland (87 %), Sweden (72 %).
(PRESUTTO et al, 2007)
The share of washing machines with a higher rated capacity has grown in the past
years. On the European market, the average washing machine load capacity has
increased from 4,8 kg in 1997 up to 5,4 kg in 2005 (CECED, 2005) and is still
increasing. In 2010, washing machines with a rated capacity between 5,5 kg and 7 kg
were the most important market segment in 10 EU countries (AT, BE, DE, ES, FR,
GB, IT, NL, PT, SE) (BERTOLDI et al., 2012). In 2012, the top selling appliances were
those with a 7 kg rated capacity (Henkel, private communication).
Figure 1-4: Average load capacity trends of household washing machines
(Data source: GfK cited from BERTOLDI et al., 2012, own representation)
1.2.4 Resource consumption for washing purposes
1.2.4.1 Electricity consumption
The residential sector accounts for 29,71 % of total electricity used, the second largest
electricity consumption sector. Within the residential sector, 7,2 % of electricity is
consumed for laundry care. This shows the importance of washing and drying in the
total electricity consumption. (BERTOLDI et al., 2012)
INTRODUCTION 8
The Eco-design preparatory study estimated the energy consumption of the washing
machine stock in 2005 to be around 51 TWh / year, with an average yearly
consumption per appliance of 295 kWh in the EU-27 households. (PRESUTTO et al,
2007)
A very comprehensive study regarding the energy consumption for washing purposes
worldwide is delivered by PAKULA AND STAMMINGER, 2010. With their study, they
covered roughly 780 million washing machines in about 2.3 billion households, which
is about one third of the world population. PAKULA AND STAMMINGER note that most
countries outside of their investigation still do their laundry washing by hand.
According to their calculated estimation, the global electricity consumption of washing
machines may be, at maximum, about 100 TWh /year of electricity. (PAKULA and
STAMMINGER, 2010)
1.2.4.2 Water consumption
Total water abstraction in the European Union (EU 27) amounts to about 247 000
million m³/year. On average, 44 % of total water abstraction in European Union is
used for energy production, 24 % for agriculture, 17 % for public water supply and
15 % for industry (DWORAK et al., 2007).
The Organization for Economic Co-operation and Development estimates that the
share of the household in the total water consumption amounts to ca. 10 % to 30 %
(OECD, 2013). Average consumption in OECD countries is about 100 000 l/year and
person equals 174 liters per person per day. According to the European Environmental
Agency, the average water consumption in Europe is between 100 liters and 320 liters,
with an average of 155 liters per person and day (EEA, 2005).
Pakula and Stamminger estimate that 20 000 000 000 m3 water is consumed worldwide
for laundry washing in a washing machine (PAKULA and STAMMINGER, 2010).
INTRODUCTION 9
1.2.5 Consumer behavior in use of washing machines
When taking into account the cradle-to-grave life cycle of a washing machine, i.e.
including the production, use and disposal phase, it becomes obvious that the use
phase is the most resource-consuming and waste-producing (Figure 1-5).
Figure 1-5: Life cycle analysis of a washing machine (Source: RÜDENAUER et al.)
Since washing machines are operated on consumer demand, their consumption of
water, energy and detergents for a washing cycle is determined mainly by
consumer-driven factors such as the frequency of washing, loading behavior, selection
of the washing temperature/program and dosing of detergents (STAMMINGER et al.,
2008).
Much research regarding the behavior of the consumer when washing laundry has
been conducted in the past years. However, much of this research was conducted by
producers of the detergent and appliance industry, and hence was partially published
or not published at all.
The most relevant studies of the European consumer washing behavior that have been
published in the past 10 years are listed below.
0
50
100
Energy
CO2
CSB
Waste
INTRODUCTION 10
2003 ARILD et al. conducted a survey with 4010 participants from Greece, the
Netherlands, Norway and Spain with the goal of finding out how the consumers handle
the washing of laundry (ARILD et al., 2003).
JÄRVI and PALOVIITA conducted interviews in 2004 and 2005 with 340, in this case 299,
people in Finland with the goal of finding out how consumers
read/understand/implement the information and instructions on detergent (JÄRVI AND
PALOVIITA, 2007).
In 2007, the University of Bonn conducted an online survey as part of a Preparatory
Study for Eco-design Requirements of Energy-using Products. A total of 2500
participants from 10 European countries took part in the survey (PRESUTTO et al, 2007).
In 2007 BERKHOLZ et al. conducted a non-representative study on behalf of the German
Federal Ministry of Economics and Technology and studied the washing behavior of
100 German households over a period of one month. The participants of the study
were actually measuring the amount of laundry, detergent and electricity consumed for
washing purposes. (BERKHOLZ et al., 2007)
STAMMINGER and GOERDELER published results of a survey conducted in 2005 with
3750 participants from all parts of Germany regarding their behavior in laundry
washing. (STAMMINGER and GOERDELER, 2007)
In 2008 and 2011, the international association for soaps, care and cleaning products
(AISE) conducted a survey with 5060 consumers in 23 European countries with an
aim to find out laundry washing behavior. (AISE, 2008; AISE, 2011)
Not all studies have had the same research question; therefore the results of different
studies cannot always be compared. However, the following data regarding the
washing frequency, loading behavior and washing temperature selection is available.
1.2.5.1 Washing frequency
The number of washing cycles depends on factors such as the washing machine’s rated
capacity or household size, loading behavior, etc. In the literature, information
INTRODUCTION 11
regarding the consumers’ behavior when using washing machines is sometimes
contradictory.
According to RÜDENAUER and GRIEßHAMMER, 164 wash cycles per year for an average
household is conducted in Germany, Austria, and Switzerland. RÜDENAUER and
GRIEßHAMMER list that the average number of washing cycles starts with 111 wash
cycles for a one-person household and increases to 211 wash cycles per year for a
four-person household (RÜDENAUER and GRIEßHAMMER, 2004)
STAMMINGER and GOERDELER published 4,5 washes per week (234 per year) as an
average household number of washing cycles in Germany. Those figures are based on
online questionnaires of more than 2000 persons. (STAMMINGER and GOERDELER, 2007)
PRESUTTO et al, state that the average washing frequency is 2,6 times per week for
single- and 6,2 for four-person households. On average, 4,9 wash cycles per household
per week, which equals on average 254 per year, are conducted. (PRESUTTO et al, 2007)
1.2.5.2 Loading of the washing machine
Many studies show that consumers do not fully use the rated capacity of their washing
machine. BERKHOLZ et al. measured that, for example in Germany, the average load of
a washing machine is 3,2 kg per wash cycle (BERKHOLZ et al., 2007).
According to PRESUTTO et al., most consumers claim to use the full loading capacity of
their washing machine, but this does not mean that the rated capacity is really used
(PRESUTTO et al, 2007).
DE ALMEIDA et al. state that the vast majority of the households always use the washing
machine at over 75 % of its capacity. (DE ALMEIDA et al., 2006)
Another measurement study shows that for an average washing machine capacity of 5
kg, consumers consider an average load of 3,7 kg to be a full load
(KRUSCHWITZ et al., 2014).
INTRODUCTION 12
1.2.5.3 Use of washing temperature and program
According to PRESUTTO et al., the average nominal washing temperature in Europe is
45,8 °C. The most used program is the 40 °C program (37 %), the second most used
temperature is 60 °C, which is 23 % of all the washes (PRESUTTO et al., 2007).
AISE publication also states that the 40 °C program is the most used program with
40 % of all the washes (AISE, 2013).
According to STAMMINGER and GOERDELER, the average washing temperature in
Germany is 46,3 °C. The most used washing temperature is 40 °C with 37 % of all
wash cycles. The second and third most used washing temperatures are 60 °C with 30
% of all washing cycles resp. 30 °C with 27 % of all washing cycles. (STAMMINGER and
GOERDELER, 2007)
1.3 Sustainability
For weighing the climatic impact of emission of different greenhouse gases, the
Intergovernmental Panel on Climate Change (IPCC) has, since its first assessment in
1990, used the Global Warming Potential (GWP). (CHANGE, 1990)
The GWP has been subjected to much criticism because of its formulation, but
nevertheless it has retained some favor because of the simplicity of its design and
application, and also its transparency compared to proposed alternatives.
(SHINE et al., 2005)
In December 1997, the Kyoto Protocol was adopted (BREIDENICH et al., 1998). It
entered into force on 16 February 2005 and for the first time it establishes legally
binding limits for 37 industrialized countries on emissions of carbon dioxide and other
greenhouse gases. (KyotoProtocol, 2013)
Kyoto Protocol set a binding reduction target for EU-15 GHG emissions of 8 % on
average for the 2008–2012 period, compared with 1990 levels. In February 2011, the
European Council reconfirmed the EU objective of reducing greenhouse gas (GHG)
emissions by 80–95 % by 2050, as compared to levels in 1990 (COMMISSION, 2011).
INTRODUCTION 13
Figure 1-6: Contribution of the different sectors to the GHG emission (Source: EEA, 2010)
The contribution of the household and services to the global GHG emission is 14,5%
(EEA, 2010). The EU objective of reducing greenhouse gas emissions can only be
achieved when all the sectors contributing to the GHG emission contribute to that goal.
By lowering the energy consumption, a total GHG emission can be achieved.
1.4 Demographic trends
According to the convergence scenario of EUROPOP2010, the EU-27’s population is
projected to increase to 525 million by 2035, peaking at 526 million around 2040, and
thereafter gradually declining to 517 million by 2060 (EUROSTAT, 2013) .
Not only is an increase of the population expected, but the number of households with
a fewer number of household members is also increasing.
According to a study published by OECD by 2025-2030, one-person households will
make up around 40 % or more of all households in the following European countries:
Austria, France, Germany, the Netherlands, Norway, Switzerland and England. The
authors of the study see the reason for this largely as a consequence of an ageing
Energy production
31,1%
Manufact. / construction
12,4% Transport 19,6%
Households / services
14,5%
Fugitive emissions
1,7%
Industrial processes
8,3%
Agriculture 9,6%
Waste 2,8%
INTRODUCTION 14
population, increase of the sole-parent household and current fertility rates and
increases in life expectancy. (OECD, 2011)
1.5 Modeling approaches
There are different approaches to model the washing machines and their processes.
Since the modeling of the washing machine is mainly done in the industry, the
published research in this field is scarce. However, a selection of different modeling
approaches is presented.
Parametrical modeling was used by WARD. In this research, the trajectory of a single
concentrated mass was parametrically modeled in order to estimate the pressure drops
that would occur on the mass as it is lifted by the baffles of the rotating washing
machine drum and then subsequently dropped and impacted upon landing. (WARD,
2000)
TERPSTRA conducted research with an aim to evaluate whether the cleaning
performance of domestic washing machines can be assessed with test soils by using
the statistical modeling of the real experimentally-generated data. (TERPSTRA, 2001)
In 2003, PARK and WASSGREN conducted a computational simulation of textile
dynamics inside a rotating drum. They used a simplified discrete element
computational model to model the movement of the textiles. The textiles were
modeled as spherical bundles, and their movement and interactions were modeled on
the basis of the macroscopic behavior of these spherical textile bundles. (PARK and
WASSGREN, 2003)
LAZAREVIĆ and VASIĆ used a mathematical modeling approach to model washing
machines, where it is seen as a conglomerate of rigid multi-body systems. The basic
properties of the washing machine are the basis for the construction of the model.
(LAZAREVIĆ and VASIĆ, 2008)
RAMASUBRAMANIAN and TIRUTHANI used computational modeling to develop firstly a
simplified 2D model, and then later a 3D model of a washing machine. The goal of the
research was, by using the computer model, to develop a better understanding of the
INTRODUCTION 15
dynamics of modern washing machines that use balance rings. (RAMASUBRAMANIAN
and TIRUTHANI, 2009)
MAC NAMARA et al. used the Positron Emission Particle Tracking (PEPT) technique,
where radioactively labeled particles are monitored. In the research, a single tracer
particle attached to a textile was monitored as it rotated and tumbled amongst other
textiles in a commercially available domestic washing machine. The aim of the
research was to understand the mechanisms by which mechanical action is imparted
onto wet textiles during washing. (MAC NAMARA et al., 2012)
IN 2005, RÜDENAUER et al. conducted a life cycle assessment for washing machines to
model the complex interaction between a product and the environment. The model
includes the life cycle of a product from the production, use and disposal phases. In the
study, RÜDENAUER et al. compare the acquisition and use of a washing machine with a
larger rated capacity to the acquisition and use of a washing machine with a rated
capacity of 5 kg under environmental and economic aspects. (RÜDENAUER et al., 2005)
The presented modeling approaches focus on a specific aspect of a washing machine
(e.g. exploring the influence of mechanics in a washing process), but none of the
models depicts the whole washing process. Furthermore, those models also do not
include the washing machine’s rated capacity, except that of RÜDENAUER et al. Finally,
the role of the consumer / household is either only rudimentary or not included in
those models at all.
INTRODUCTION 16
OBJECTIVE 17
2 Objective
On the European market at present, two opposing trends can be observed. On one
hand, an increase of the average load size of the washing machines that are sold on the
market is observed. On the other hand, the demographic structure of the European
households is changing, resulting in a decrease of the average household size and
hence results in a reduced amount of laundry to be washed.
In addition to those two opposing trends, it should be kept in mind that consumers at
present do not fully use the rated capacity of their washing machines, and consider a
partial load level as a full load.
Those considerations lead to the question: “What kind of washing behavior is needed,
so that the usage of washing machines with a higher rated capacity has a low impact
on the environment?”
In order to answer that question, the following needs to be done:
Firstly, a model of a virtual washing machine that is based on average and
typical data of washing machines available on the market shall be developed.
The virtual washing machine should be flexible, so that the input parameters
selected by the consumer can be varied.
Secondly, a virtual washing household that incorporates various washing
behavioral parameters shall be developed.
Thirdly, a simulation of the usage of the virtual washing machine by the virtual
washing households shall be developed. By conducting parallel simulations and
by varying device-, household-, and behavioral parameters, optimal parameter
combinations with low environmental impact shall be determined and hence
conclusions regarding an optimal consumer behavior are to be drawn.
OBJECTIVE 18
MATERIAL AND METHODS 19
3 Material and methods
All material and methods used for testing the washing machines are based on the
experimental setup required in EN60456:2005.
The framework of EN60456:2005 is broadened and tests with a load of 25 % and 75 %
as well as tests with detergent under- and overdose are included. Those cases are
marked accordingly. In some cases, the EN60456:2010 is applied and also those cases
are marked accordingly.
3.1 Material
3.1.1 Tested washing machines
All tested washing machines are front loading washing machines and are prepared in
accordance with the manufacturer's specified safety instructions and installed in
accordance with EN60456:2005.
Table 3-1: List of tested washing machines
Manufacturer and washing machine model rated capacity Ident. Nr:
Miele Novotronic W1514 5 kg WM1 Indesit IWB 5125 5 kg WM2
BOSCH Maxx6 Eco Wash WAE2834P 6 kg WM3
Bauknecht WA UNIQ 714FLD 7 kg WM4
AEG Öko Lavamat 76850 A 7 kg WM5
BOSCH Logixx8 Vario Perfekt WAS32792 8 kg WM6
Haier HW-F1481 8 kg WM7
Indesit PWE 8168W 8 kg WM8
Bauknecht WAB-1210 11 kg WM9
3.1.2 Washing machine used for standardization and neutralization
MIELE W1514 NOVOTRONIC and WASCATOR CLS are used for the normalization process
of the test load. MIELE NOVOTRONIC W1514 program software is modified so that it
complies with the standard procedure as described in EN60456:2005.
MATERIAL AND METHODS 20
Table 3-2: Equipment used for the normalization process of the load
Washing machine washing machines tested
W1514 Novotronic WM1, WM3, WM4, WM5, WM6 Wascator WM2, WM7, WM8, WM9
3.1.3 Test load
The test load consists of the base load and the soil strips as specified. Base load is used
in accordance with EN60456:2005 and consists of cotton bed sheets, cotton
pillowcases, and cotton towels. Soiled test trips are in accordance with EN60456:2010
and were manufactured by “EMPA Testmaterialien”.
Table 3-3: Soil strips and respective batch number used for the tests
EMPA Batch number Washing machines tested
Batch 21 WM1, WM3, WM4, WM6 Batch 27 WM5 Batch 35 WM2, WM7, WM8 Batch 45 WM9
3.1.4 Detergent
Reference detergent A* is used in the test as specified by the EN50456:2005. During
the testing time, all three components are stored separately and used within the expiry
date as stated in the documentation provided by the manufacturer.
Table 3-4: Detergent
Component batch Nr.
Washing machines tested base powder sodium
perborate tetrahydrate
bleach activator (TAED)
WM1, WM3, WM5, WM6 167-513 237-394 24704603
WM2, WM4, WM7, WM8, WM9 237-970 287-984 26746203
MATERIAL AND METHODS 21
3.1.5 Software
Table 3-5 lists all software used.
Table 3-5: Overview of software used
Software name Used for
Matlab 2010a Simulation of a washing process IBM SPSS Statistics 21 Multivariate statistics i.e. Multiple linear regression Colorimeter software Evaluation of the EMPA soil strips Alborn Data logger software used to monitor and record the test
experiment
3.2 Methods
3.2.1 Washing machines tests
The framework of EN60456:2005 is extended so that some test parameters such as
temperature, detergent dosage and load size are varied.
In addition, differing from EN60456:2005 in which five repetitions of each parameter
setting are required, in this case one repetition is conducted for each parameter setting.
3.2.1.1 Load
The load is varied so that tests with 25 %, 50 %, 75 % and 100 % of the rated washing
machine load capacity were conducted. Furthermore, tests with no load were
performed in order to simulate a very small load. Table 3-6 shows the loading
scenarios for different washing machines.
Table 3-6: Loading scenarios for different washing machines’ rated capacities
WM rated capacity
Load size 25 % in kg
Load size 50 % in kg
Load size 75 % in kg
Load size 100 % in kg
5 kg 1,25 2,5 3,75 5 6 kg 1,5 3 4,5 6 7 kg 1,75 3,5 5,25 7 8 kg 2 4 6 8 11 kg 2,75 5,5 8,25 11
MATERIAL AND METHODS 22
3.2.1.2 Detergent dosing
In order to reflect a more consumer-relevant behavior in the testing procedure, the
amount of the nominal dose of detergent was calculated as specified in
EN60456:2010.
Nominal dosing:
To simulate the over- and under-dosing, the following dosages are included.
Overdosing:
Under dosing:
Prior to the dosing the detergent, the detergent dispenser is cleaned and dried.
3.2.1.3 Temperature/program
The washing temperature is varied so that the washing program at 30 °C, 40 °C, and
60 °C are conducted. Combining all varied parameters results in a total of 39 tests
conducted for one single washing machine. Washing program is “cotton” and the spin
speed is 1400 rpm. During the washing cycle the water temperature in the sump is
monitored by a sensor placed in the space between the inner and outer drum at the
bottom of the washing machine’s drum.
Table 3-7: Test design and variation of the parameters
Load size
Temperature Number of
30 °C 40 °C 60 °C tests
0 % No detergent No detergent No detergent 3
25 % Over dose
Nominal dose Under dose
Over dose Nominal dose Under dose
Over dose Nominal dose Under dose
9
50 % Over dose
Nominal dose Under dose
Over dose Nominal dose Under dose
Over dose Nominal dose Under dose
9
75 % Over dose
Nominal dose Under-dose
Over dose Nominal dose Under dose
Over dose Nominal dose Under dose
9
100 % Over dose
Nominal dose Under dose
Over dose Nominal dose Under dose
Over dose Nominal dose Under dose
9
MATERIAL AND METHODS 23
The experimental setup is based on the following recurring test scheme based on
EN60456:2005 (Figure 3-1).
Figure 3-1: Example of a testing procedure on an example of a 25 % load
3.2.1.4 Normalization and conditioning
In accordance with the EN60456:2005, the normalization process is conducted in
batches of 3,75 kg. If the quantity exceeded the quantity of 3,75 kg, the laundry
amount is divided into smaller load sizes.
Conditioning is conducted as described in EN60456:2005. The individual items of
laundry are left for 24 hours on a rack. All items are separately hung on, so that a
circulation of the air is ensured.
Normalizing and conditioning
Detergent dosage 50 %
Cotton 30 °C Cotton 40 °C Cotton 60 °C
Detergent dosage 100 %
Cotton 30 °C Cotton 40 °C Cotton 60 °C
Detergent dosage 150 %
Cotton 30 °C Cotton 40 °C Cotton 60 °C
Normalizing
Normalizing
MATERIAL AND METHODS 24
3.2.1.5 Reproduction tests
Every constellation of the parameters is tested once. In order to test the reproducibility
of the results, every washing machine is tested in so-called reproduction tests. For this
reason, three tests in accordance with EN60456:2005 with a full load, using the
washing program "cotton 60 °C", and with a detergent dosage of 100 % are conducted.
3.2.1.6 Evaluation of the soil strips
Upon completion of a test, the test load is removed no later than ten minutes after the
completion of the washing process. The attached soil strips are separated. Test loads
without the soil strips is then weighted and dried. The separated soil strips are air-
dried, ironed, and evaluated by measuring the tristimulus Y reflectance in accordance
with EN60456:2005.
3.2.1.7 Calculation the washing performance index
According to the standard EN60456:2005, the CIE Y values calculated for every
washing machines test is set in proportion to those of a reference washing machine.
In EN60456:2005, the reference washing machines tests are conducted by washing
5 kg of laundry in a reference washing machine and using 180 g of the reference
detergent.
In EN60456:2010, the reference washing machine tests are conducted the same as in
EN60456:2005, except that the detergent dosage is 110 g.
In this research, the reference washing machine tests are not conducted. Instead, the
documentation provided by the soil strip producer “Empa Testmaterialien” is used.
The values in the documentation are provided only in accordance with EN60456:2005
for 180 g and 135 g. Based on those values, the CIE Y values for 110 g are
extrapolated.
MATERIAL AND METHODS 25
Table 3-8: CIE Y values of different batches and extrapolated values for 110g of detergent
Batch Number
CIE Y values for 180 g
CIE Y values for 135 g
Extrapolated Y CIE values for 110g
21 355,1 345,7 340,5 27 353,6 342,9 337,0 35 353,5 340,7 333,6 45 348,7 336,1 329,1
3.2.1.8 Testing conditions
All testing conditions are maintained as defined in EN60456:2005
Table 3-9: Testing conditions in accordance with EN60456:2005
Parameter Interval
Ambient temperature 23 ± 2 °C Water temperature 15 ± 2 °C Water pressure 2,4 ± 0,5 bar Water hardness 2,5 ± 0,2 mmol / L Power supply voltage 230 V ± 1 % Power supply frequency 50 Hz ± 1 %
3.2.2 Construction of the model of a virtual washing machine
During the washing machine tests, input parameters (independent variables) are:
washing temperature, load size, washing machine’s rated capacity, duration of the
main wash and amount of detergent. The output parameters (dependent variables) are:
Energy consumption, water consumption, washing performance and washing time.
By using this data, a model of a virtual washing machine is constructed. This model
consists of a set of multiple linear regression equations that puts into relation the input
and output parameters, and hence can be used to predict the amount of resources
consumed during a single washing cycle (detergent, water and energy).
MATERIAL AND METHODS 26
The basis for the construction of the virtual washing machine model is a general
equation for multiple linear regressions.
𝑌 𝑋 𝑋 (3-1)
Where is:
𝑌 𝑑𝑒𝑝𝑒𝑛𝑑𝑒𝑛𝑡 𝑣𝑎𝑟𝑖𝑎𝑏𝑙𝑒
𝑋 𝑋 𝑋 𝑖𝑛𝑑𝑒𝑝𝑒𝑛𝑑𝑒𝑛𝑡 𝑣𝑎𝑟𝑖𝑎𝑏𝑙𝑒𝑠
𝑝𝑎𝑟𝑎𝑚𝑒𝑡𝑒𝑟𝑠 𝑎𝑠𝑠𝑜𝑐𝑖𝑎𝑡𝑒𝑑 𝑤𝑖𝑡 𝑖𝑛𝑑𝑒𝑝𝑒𝑛𝑑𝑒𝑛𝑡 𝑣𝑎𝑟𝑖𝑎𝑏𝑙𝑒
Based on the eq. (3-1) and the input parameters, three different multiple regression
equations are developed. Each of the equations is used to predict one of the consumed
resources (i.e. amount of the detergent, water and energy consumed for a single
washing cycle).
3.2.2.1 Calculations of the consumption in CO2 equivalents
In order to be able to compare different resources (water, detergent and energy), its
respective amounts are converted into the CO2 equivalents by using the conversion
values as presented in Table 3-10.
Table 3-10: Overview of CO2 conversion factors
Factor Gram CO2 per unit Unit
CO2WATER1 6,16 liter
CO2ENERGY2 601 kWh
CO2DETERGENT3 1,7 gram
For the calculation of CO2 equivalents for detergent consumed during a single washing
cycle ( ), the following equation is used:
1 Source: Jungbluth, N., des Gas, S. V. & Wasserfaches, S. (2006) Vergleich der Umweltbelastungen von
2 Source: Icha, P. (2013) Entwicklung der spezifischen Kohlendioxid-Emissionen des deutschen Strommix in
den Jahren 1990 bis 2012. Climate Change, Umweltbundesamt, 07/2013.
3 Source: Henkel, private communication
MATERIAL AND METHODS 27
𝐶𝑂𝐸 CO DETERGENT (3-2)
Where is:
𝑎𝑚𝑜𝑢𝑛𝑡 𝑜𝑓 𝑑𝑒𝑡𝑒𝑟𝑔𝑒𝑛𝑡 𝑐𝑜𝑛𝑠𝑢𝑚𝑒𝑑 𝑑𝑢𝑟𝑖𝑛𝑔 𝑎 𝑠𝑖𝑛𝑔𝑙𝑒 𝑤𝑎𝑠𝑖𝑛𝑔 𝑐𝑦𝑐𝑙𝑒
For the calculation of CO2 equivalents for water consumed during a single washing
cycle ( ), the following equation is used:
𝐶𝑂𝐸 CO WATER (3-3)
Where is:
𝑋 𝑎𝑚𝑜𝑢𝑛𝑡 𝑜𝑓 𝑑𝑒𝑡𝑒𝑟𝑔𝑒𝑛𝑡 𝑐𝑜𝑛𝑠𝑢𝑚𝑒𝑑 𝑑𝑢𝑟𝑖𝑛𝑔 𝑎 𝑠𝑖𝑛𝑔𝑙𝑒 𝑤𝑎𝑠𝑖𝑛𝑔 𝑐𝑦𝑐𝑙𝑒
For the calculation of CO2 equivalents for energy consumed during a single washing
cycle ( ), the following equation is used:
𝐶𝑂𝐸 CO ENERGY (3-4)
Where is:
For the calculation of total CO2 equivalents consumed during a single washing cycle
( ), the following equation is used:
𝐶𝑂𝐸 𝐶𝑂𝐸 𝐶𝑂𝐸 𝐶𝑂𝐸 (3-5)
The following figure shows a schematic of the model construction
MATERIAL AND METHODS 28
DetergentWater
consumption
Energy
consumption
Input and output parameter
CO2 conversion
CO2 usage for one washing cycle
CO2
conversion
CO2
conversion
Figure 3-2: Schematic of the mathematical model construction of a washing machine (own representation)
3.2.3 Construction of the model of virtual washing household
In order to simulate the usage of the virtual washing machine, the following concept of
virtual washing household is presented.
It is assumed that the usage of the washing machine is defined by:
1. Washing machine related factors (washing machine’s rated capacity and
duration of the washing programs)
2. Household related factors, such as the household size, amount and type of
laundry that has to be washed per person and week.
3. Washing behavior related factors (e.g. washing temperature, loading behavior
and dosing behavior )
Simulation of a routine structure as an example for a washing of laundry that has to be
washed in a 30 °C program is presented in Figure 3-3. Analogously, the simulation
structure can be applied to a 40 °C and 60 °C washing program.
MATERIAL AND METHODS 29
Percentage of 30°C
laundry in percent
Number
of
persons
Washing cycle 30°C
Remains
of laundryIf LA30 ≥ LF30
YES
Washing machine load
size in kg: (WMLS)
Loading behavior for
30°C (LB30)
Counter
of
laundry
remains
If counter of laundry
remains
= MLWT
Maximal
laundry waiting
time in weeks
(MLWT)
NO
YES
Set counter of laundry
remains to zero
Laundry amount 30°C
(LA30)NO
SET LA30
TO:
LA30 – LF30
Weekly additional
laundry per person in kg
Load factor 30 (LF30)=
WMLS*LB30
Figure 3-3: Example of a schematic of the simulation
Simplified, the simulation can be described by the following five steps:
1) Parameter induction
a. Setting of the washing machine’s rated capacity
b. Setting of the number of persons in household
c. Setting the amount of laundry that has to be washed per person and per
week.
d. Setting of the maximal laundry waiting time (MLWT)
e. Set the week counter to zero
2) Calculation prior to wash
a. Determine the amount of rest load from previous week. In the first week
this value is zero.
b. Calculation of the washing cycle load amount by multiplying the
washing machine’s rated capacity with the loading factor.
c. Calculation of the available amount of laundry that has to be washed
3) Washing process simulation
MATERIAL AND METHODS 30
a. If the available amount of laundry that has to be washed is lower than
washing cycle load amount, continue to (4).
b. If the available amount of laundry that has to be washed is equal to or
higher than washing cycle load amount, conduct the washing simulation.
Repeat this step until the available amount of laundry is lower than the
washing cycle load amount. The remaining amount of laundry is added
to the next week’s amount of laundry.
4) Add one week to the week counter.
5) Check whether the duration of the simulation has been reached – if not, restart
from Step (2).
6) If yes , end of the simulation.
With every week, the new amount of laundry per person is introduced into the
simulation.
3.2.4 Combination of virtual washing household and virtual washing machine
Simulation of long-term usage is conducted by combining the model of the virtual
washing household and the model of the virtual washing machine.
By using Matlab software, a program that combines those two segments is
programmed so that the following input parameters can be varied:
- Washing machine’s rated capacity
- Number of persons in household
- Amount of laundry per person
- Type of laundry per person
- Maximal laundry waiting time
- Loading behavior for certain types of laundry
- Duration of the simulation
MATERIAL AND METHODS 31
3.2.4.1 Correction of the detergent amount
It is to be expected that in some cases, when a small load is washed in a washing
machine with a high rated capacity, the calculated amount of detergent is very low.
However, consumers always dose a certain amount of detergent. In order to include
this consumer behavior in the model, the following convention is implemented in the
yearly simulation:
When the amount of calculated detergent for a single wash is lower than 40 g
(EN60456:2010 base amount of detergent), the calculated amount of detergent is
automatically corrected to 40 g.
3.2.4.2 Scenario used for simulation
The simulations are conducted by using the following general simulations parameters:
Duration of the simulation = 52 weeks
Weekly additional laundry = 4 kg per person
The average composition of the load (KRUSCHWITZ et al., 2014)
Washing load at 30 °C = 23 % of total load
Washing load at 40 °C = 46 % of total load
Washing load at 60 °C = 31 % of total load
The maximal loading factor for:
30 °C washing cycle = 50 % of the rated capacity
40 °C washing cycle = 70 % of the rated capacity
60 °C washing cycle = 90 % of the rated capacity
MATERIAL AND METHODS 32
3.2.5 Average values calculations
For the calculation of the average values, the following formula was used:
(3-6)
Where is:
�̅� 𝑎𝑟𝑖𝑡𝑚𝑒𝑡𝑖𝑐 𝑚𝑒𝑎𝑛 𝑥 𝑜𝑏𝑠𝑒𝑟𝑣𝑒𝑑 𝑣𝑎𝑙𝑢𝑒𝑠 𝑛 𝑛𝑢𝑚𝑏𝑒𝑟 𝑜𝑓 𝑜𝑏𝑠𝑒𝑟𝑣𝑎𝑡𝑖𝑜𝑛𝑠
RESULTS 33
4 Results
In this chapter, all data received by the experiments, mathematical modeling, and
simulations are worked out and presented.
4.1 Results of the washing machines tests
An overview of the data of the washing machines tests is presented.
4.1.1 Water consumption
Figure 4-1: Water consumption versus load of nine washing machines - washing temperature is 60 °C
Water consumption increases with an increase of the load size for all washing
machines tested (Figure 4-1). Comparison of slopes indicates that washing machines
differ in their ability to adapt its water consumption to the amount of load. The slope
of the WM3 shows that the load size has the lowest influence on water consumption.
Other washing machines have quantity controls that are more sensitive to a variation
of the load.
0 25 50 75 1000
20
40
60
80
100
Load in percent
Wa
ter
co
nsu
mp
tio
n in
lite
r
WM1 (5 kg)
WM2 (5 kg)
WM3 (6 kg)
WM4 (7 kg)
WM5 (7 kg)
WM6 (8 kg)
WM7 (8 kg)
WM8 (8 kg)
WM9 (11 kg)
RESULTS 34
Figure 4-2: Comparison between the specific water consumption and the load size
With an increase of the load, specific water consumption decreases. Variations in
specific water consumption are lowest when the washing machine is fully loaded, and
highest when the washing machine is loaded with 25 % of the rated capacity. When
washing machines are underloaded, the differences in specific water consumption for
washing nearly same amount of load vary to up to twice (Figure 4-2).
Figure 4-3: Water consumption versus load amount - washing temperature is 60 °C
0 2 4 6 8 100
5
10
15
20
25
30
Load in kilogram
Sp
ecific
Wa
ter
co
nsu
mp
tio
n in
l/k
g
WM1 (5 kg)
WM2 (5 kg)
WM3 (6 kg)
WM4 (7 kg)
WM5 (7 kg)
WM6 (8 kg)
WM7 (8 kg)
WM8 (8 kg)
WM9 (11 kg)
0 25 50 75 1000
20
40
60
80
100
120
Load in percent
Wa
ter
co
nsu
mp
tio
n d
ecre
ase
in
pe
rce
nt
WM1 (5 kg)
WM2 (5 kg)
WM3 (6 kg)
WM4 (7 kg)
WM5 (7 kg)
WM6 (8 kg)
WM7 (8 kg)
WM8 (8 kg)
WM9 (11 kg)
RESULTS 35
Setting the water consumption of a fully-loaded washing machine as 100 % reveals
that water reduction is not proportional to the load reduction (Figure 4 3).
A load decrease of 50 % leads, in the best case, to a water consumption decrease of
less than 40 % (in the worst case, the decrease is less than 5 %).
Table 4-1: Ratio between the main wash water consumption and the total water consumption (mean values), in dependence of the detergent dosage
Detergent dose in percent of a nominal dose
50 % 100 % 150 % Mean
WM1 1:3,4 1:3,4 1:3,3 1:3,4 WM2 1:3,3 1:3,3 1:3,3 1:3,3 WM3 1:4,0 1:3,9 1:3,7 1:3,9 WM4 1:4,0 1:4,0 1:4,0 1:4,0 WM5 1:3,5 1:3,5 1:3,6 1:3,5 WM6 1:4,1 1:4,1 1:4,1 1:4,1 WM7 1:3,4 1:3,3 1:3,3 1:3,3 WM8 1:3,2 1:3,1 1:3,2 1:3,2 WM9 1:3,3 1:3,3 1:3,3 1:3,3
Mean
1:3,5
Table 4-2: Ratio between the main wash water consumption and the total water consumption (mean values), in dependence of the load size
Washing machine load in percent of rated capacity
25 % 50 % 75 % 100 % Mean
WM1 1:3,0 1:3,4 1:3,5 1:3,6 1:3,4 WM2 1:3,8 1:3,4 1:3,1 1:2,9 1:3,3 WM3 1:4,8 1:4,0 1:3,4 1:3,3 1:3,9 WM4 1:3,8 1:3,8 1:3,8 1:4,5 1:4,0 WM5 1:3,5 1:3,9 1:3,4 1:3,3 1:3,5 WM6 1:4,3 1:4,2 1:3,9 1:3,9 1:4,1 WM7 1:3,6 1:3,5 1:3,2 1:3,0 1:3,3 WM8 1:3,5 1:3,3 1:3,0 1:2,9 1:3,2 WM9 1:3,4 1:3,3 1:3,2 1:3,2 1:3,3
Mean
1:3,5
The ratio values, in dependence of the load size, show the lowest mean values in the
case of the washing machine WM8 (1:3,2) and the highest values in the case of the
WM6. The mean ratio is 1:3,5.
RESULTS 36
4.1.2 Energy consumption
Figure 4-4: Energy consumption in kWh versus load size. Washing temperature 60 °C
Similar to the water consumption, the energy consumption increases with an increase
of the load size. WM4 is an exception and consumes at the load level of 25 % more
than when it is fully loaded (Figure 4-4).
Figure 4-5: Energy consumption versus load amount - washing temperature is 60 °C
0 2 4 6 8 100
0.5
1
1.5
2
Load in kilogram
Ene
rgy c
on
sum
ption
in k
Wh
WM1 (5 kg)
WM2 (5 kg)
WM3 (6 kg)
WM4 (7 kg)
WM5 (7 kg)
WM6 (8 kg)
WM7 (8 kg)
WM8 (8 kg)
WM9 (11 kg)
0 25 50 75 1000
20
40
60
80
100
120
Load in percent
Ene
rgy c
on
sum
ption
decre
ase in p
erc
en
t
WM1 (5 kg)
WM2 (5 kg)
WM3 (6 kg)
WM4 (7 kg)
WM5 (7 kg)
WM6 (8 kg)
WM7 (8 kg)
WM8 (8 kg)
WM9 (11 kg)
RESULTS 37
Setting the energy consumption of a fully loaded washing machine as 100 % reveals
that energy reduction is not proportional to the load reduction. A decrease of the load
by 50 % results in a decrease of energy consumption of maximally 20 %.
Furthermore, WM6 and WM9 consume 20 % more energy when underloaded (75 % or
the rated capacity) than when fully loaded. WM4 consumes 10 % more energy when
underloaded (25 % of the rated capacity) than when fully loaded.
4.1.3 Washing performance
Figure 4-6: Index of washing performance versus load for cotton 60 °C
With an increase of the load size, the washing performance decreases. WM3 shows the
lowest washing performance index values for all loading sizes (Figure 4-6).
25 50 75 1000.75
0.8
0.85
0.9
0.95
1
1.05
1.1
1.15
Load in percent
Inde
x o
f w
ashin
g p
erf
orm
an
ce
WM1 (5 kg)
WM2 (5 kg)
WM3 (6 kg)
WM4 (7 kg)
WM5 (7 kg)
WM6 (8 kg)
WM7 (8 kg)
WM8 (8 kg)
WM9 (11 kg)
RESULTS 38
Figure 4-7: Index of washing performance vs. energy consumption. From left to right the energy values indicate the machines' energy use for 30 °C, 40 °C and 60 °C washing
programs
With an increase of the washing temperature, the energy consumption and the washing
performance increases. In the case of WM1, an increase of the washing temperature
from 30 °C to 40 °C results in an increase of the energy consumption of 0.13 kWh and
the washing performance increases 0,003 index points.
In the case of the WM8, an increase of the washing temperature from 30 °C to 40 °C
results in an increase of the energy consumption of 0,63 kWh and a washing
performance increase of 0,207 index points. An increase of the washing temperature
from 40 °C to 60 °C results in an increase of the energy consumption of 0,24 kWh and
an increase of the washing performance of 0,018 washing performance index points.
(Figure 4-7).
0 0.5 1 1.50.75
0.8
0.85
0.9
0.95
1
1.05
1.1
1.15
Energy consumption in kWh
Ind
ex o
f w
ash
ing
pe
rfo
rma
nce
WM1 (5 kg)
WM2 (5 kg)
WM3 (6 kg)
WM4 (7 kg)
WM5 (7 kg)
WM6 (8 kg)
WM7 (8 kg)
WM8 (8 kg)
WM9 (11 kg)
RESULTS 39
Figure 4-8: Index of washing performance vs. detergent dosage
Washing performance varies between different washing machines. An adjustment of
the washing performance can also be done by varying the amount of the detergent.
Comparison of the slopes shows a slightly higher loss in performance when the dosage
is reduced from 100 % to 50 % than from 150 % to 100 % (Figure 4-8).
Table 4-3: Overview of average washing performance achieved at different washing temperatures
Washing temperature
Average washing performance at specific temperature
Washing performance setting in the simulation
30 °C 0,9288
0,93 40 °C 0,9984
1,00
60 °C 1,0449
1,04
4.1.4 Duration of the main wash
Comparison of average main washing duration data shows a large variety among
different washing machines types and nominal washing temperatures. With an increase
of the washing temperature, the duration of the main wash increases as well in most
cases. The lowest values are reached by the washing machine WM3 at 30 °C (18
minutes) and the highest values are reached by WM9 at 60 °C (173 minutes).
50 100 1500.75
0.8
0.85
0.9
0.95
1
1.05
1.1
1.15
Detergent dosage in percent
Ind
ex o
f w
ash
ing
pe
rfo
rma
nce
WM1 (5 kg)
WM2 (5 kg)
WM3 (6 kg)
WM4 (7 kg)
WM5 (7 kg)
WM6 (8 kg)
WM7 (8 kg)
WM8 (8 kg)
WM9 (11 kg)
RESULTS 40
Table 4-4: Overview of different average durations of the main wash at the following washing temperatures
Duration of the main wash cycle in minutes at the
following temperatures (average values)
30 °C 40 °C 60 °C
WM1 56 56 55 WM2 39 82 82 WM3 18 25 37 WM4 65 72 83 WM5 65 66 81 WM6 74 86 94 WM7 61 61 72 WM8 31 160 156 WM9 156 158 173
4.1.5 Washing temperature: nominal versus actual washing temperature
The washing temperature set on the washing machine (nominal washing temperature)
and the washing temperature measured by the washing machines sensor (actual
washing temperature) do not always match. In the case of the nominal temperature of
30 °C, the average actual temperature values range between 26 °C and 35 °C. In the
case of a nominal temperature of 40 °C, the average actual temperature values range
between 39 °C and 48 °C, and in the case of nominal temperature of 60 °C, the
average actual temperatures range between 49 °C and 63 °C (Table 4-5).
Table 4-5: Overview of average actual washing temperatures that were achieved instead of the respective nominal temperature
Average actual washing temperatures in °C
30 °C 40 °C 60 °C
WM1 29 38 56 WM2 35 48 59 WM3 33 44 63 WM4 29 40 56 WM5 30 39 55 WM6 26 41 56 WM7 27 37 57 WM8 29 43 51 WM9 32 39 49
RESULTS 41
4.2 Construction of model of virtual washing machine
The virtual washing machine model consists of a set of equations, each used to
calculate one of the resources consumed during a washing cycle (water, energy and
detergent). Figure 4-9 shows a schematic (based on Figure 3-3) on how the virtual
washing machine is constructed.
Water
consumption
Energy
consumption
CO2 usage for one washing cycle
Load,
washing
machine’s
rated capacity
Temperature,
main wash
duration
CO2
conversion
CO2
conversion
Detergent
Washing performance,
temperature, load, main
wash duration
CO2 conversion
Figure 4-9: Schematic of a construction of a virtual washing machine based on the data received during the washing machine tests
4.2.1 Water consumption equation
Multiple linear regression analysis (Table 4-6) was used to develop a model for
predicting water consumption from load size and rated capacity. The two-predictor
model is able to account for 88 % of the variance in water consumption.
RESULTS 42
Table 4-6: Summary statistics, correlations, and results from the regression analysis (water consumption)
multiple regression weights
Variable mean std correlation with
WC b β
Water consumption (WC) 14,772 5,1606
Load size (LS) 4,2 2,571 0,929*** 1,725*** 0,860
WM Rated capacity (WMRC) 7,2 1,77 0,527*** 0,476*** 0,162
Constant 4,116
R = 0,940
R2 = 0,884
R2Adjusted = 0,883
F = 1359,228***
* p < 0,05 ** p < 0,01 ***p<0,001
Tests to see if the data met the assumption of collinearity indicated that
multicollinearity is not a concern: Load size (Tolerance = 0,820, VIF = 1,220), rated
capacity (Tolerance = 0,820, VIF = 1,220).
The histogram of standardized residuals indicated that the data contained
approximately normally distributed errors, as did the normal P-P plot of standardized
residuals, which showed points that were not completely on the line, but close. The
scatterplot of standardized residuals showed that the data met the assumptions of
homogeneity of variance and linearity.
The general regression equation (3-1), in combination with the variables selected by
the multiple regression analysis, is used to construct a model. The final equation for
predicting the water consumption during the main wash is:
𝑪𝑾 𝟒 𝟏𝟏𝟔 𝟏 𝟕𝟐𝟓 𝐋𝐎𝐀𝐃 𝟎 𝟒𝟕𝟔 𝑾𝑴𝑽 (4-1)
Where is:
LOAD 𝑎𝑚𝑜𝑢𝑛𝑡 𝑜𝑓 𝑙𝑎𝑢𝑛𝑑𝑟𝑦 𝑖𝑛 𝑘𝑔
𝑊𝑀𝑉 𝑟𝑎𝑡𝑒𝑑 𝑐𝑎𝑝𝑎𝑐𝑖𝑡𝑦 𝑖𝑛 𝑘𝑔 𝐶𝑊𝑚𝑤 𝑤𝑎𝑡𝑒𝑟 𝑐𝑜𝑛𝑠𝑢𝑚𝑝𝑡𝑖𝑜𝑛 𝑑𝑢𝑟𝑖𝑛𝑔 𝑡𝑒 𝑚𝑎𝑖𝑛 𝑤𝑎𝑠
RESULTS 43
The ratio between the water consumed during the main wash to total water
consumption is 1:3,5 (Table 4-1 and Table 4-2), so that the equation for calculation of
the total amount of water consumed for a single washing cycle ( ) is the
following:
𝑪𝑾 𝑪𝑾 𝟑 𝟓 (4-2)
Combining the eq. (4-1) and the eq. (4-2) equation (4-3) results:
𝑪𝑾 𝟑 𝟓 (𝟒 𝟏𝟏𝟔 𝟏 𝟕𝟐𝟓 𝐋𝐎𝐀𝐃 𝟎 𝟒𝟕𝟔 𝑾𝑴𝑽) (4-3)
4.2.2 Energy consumption equation
Analogous to the construction of the equation for calculating the water consumption,
the equation for calculating energy consumption is constructed. Multiple linear
regression analysis is used (Table 4-7) to develop a model for predicting energy
consumption based on water consumption, washing temperature and the duration of
the main wash. The three-predictor model is able to account for 92 % of the variance
in energy consumption, F (3, 351) = 1323,465; p < 0,001.
Table 4-7: Summary statistics, correlations and results from the regression analysis (energy consumtion)
multiple regression weights
Variable mean std correlation with WC
b β
Energy consumption (EC) 0,525 0,3157
Water consumption (WC) 14,74 5,021 0,470*** 0,02246*** 0,357 Washing temperature (WT) 41,90 11,115 0,743*** 0,02040*** 0,720
Duration of main wash (DMW) 78,95 42,994 0,642*** 0,00247*** 0,337
Constant -0,836
R 0,959
R2 0,919
R2Adjusted 0,918
* p < 0,05 ** p < 0,01 ***p<0,001
RESULTS 44
Table 4-8: Correlations between predictor variables
EC WC WT DMW
Energy consumption (EC) Water consumption (WC) 0,470***
Washing temperature (WT) 0,743*** -0,09*
Duration of main wash (DMW) 0,642*** 0,527*** 0,162***
* p < 0,05 ** p < 0,01 ***p<0,001
Tests to see if the data met the assumption of collinearity indicated that
multicollinearity is not a concern: Water consumption in the main wash (Tolerance =
0,690, VIF = 1,449), washing temperature (Tolerance = 0,931, VIF = 1,074) duration
of the main wash (Tolerance = 0,678, VIF = 1,476).
The histogram of standardized residuals indicated that the data contained
approximately normally distributed errors, as did the normal P-P plot of standardized
residuals, which showed points that were not completely on the line, but close. The
scatterplot of standardized residuals showed that the data met the assumptions of
homogeneity of variance and linearity.
Based on the results of the multiple regression analysis, the final equation to predict
the energy consumption is constructed. The general regression equation (3-1), in
combination with the variables selected by the multiple regression analysis, is used to
construct a model. The final equation for predicting the energy consumption during the
main wash is:
𝑪 𝟎 𝟖𝟓𝟔 𝟎 𝟎𝟐 𝑴 𝟎 𝟎𝟐𝟒 𝑪𝑾 𝟎 𝟎𝟎𝟐𝟓 𝑴𝑾 (4-4)
Where is:
𝐶𝐸 𝑎𝑚𝑜𝑢𝑛𝑡 𝑜𝑓 𝑒𝑛𝑒𝑟𝑔𝑦 𝑐𝑜𝑛𝑠𝑢𝑚𝑒𝑑 𝑑𝑢𝑟𝑖𝑛𝑔 𝑡𝑒 𝑚𝑎𝑖𝑛 𝑤𝑎𝑠 𝑖𝑛 𝑘𝑊 𝑇𝐸𝑀𝑃 𝑎𝑐𝑡𝑢𝑎𝑙 𝑤𝑎𝑠𝑖𝑛𝑔 𝑡𝑒𝑚𝑝𝑒𝑟𝑎𝑡𝑢𝑟𝑒 𝐶𝑊 𝑎𝑚𝑜𝑢𝑛𝑡 𝑜𝑓 𝑤𝑎𝑡𝑒𝑟 𝑐𝑎𝑙𝑐𝑢𝑙𝑎𝑡𝑒𝑑 𝑏𝑦 𝑢𝑠𝑖𝑛𝑔 𝑒𝑞 10 𝑀𝑊𝐷 𝑚𝑎𝑖𝑛 𝑤𝑎𝑠 𝑑𝑢𝑟𝑎𝑡𝑖𝑜𝑛 𝑖𝑛 𝑚𝑖𝑛𝑢𝑡𝑒𝑠
RESULTS 45
The energy consumed during the spin phase, as well the energy consumed in
standby / left on/off mode, is not included in the total energy consumption.
4.2.3 Detergent consumption equation
Analogous to the water and energy consumption prediction equation, the multiple
linear regression analysis is used to develop a model for predicting the washing
performance index from independent variables: load size, detergent, actual washing
temperature and the duration of the main wash.
Basic descriptive statistics and regression coefficients are shown in Table 4-9. The
four-predictor model is able to account for 82 % of the variance in the washing
performance index.
Table 4-9: Summary statistics, correlations and results from the regression analysis (detergent consumption)
multiple regression weights
Variable mean std correlation with
WP b β
Washing performance (WP) 0,992 0,095
Load size 4,5 2,39 -0,255*** -0,034584*** -0,868 Detergent 93,9 48,96 0,270*** 0,001194*** 0,618 Actual washing temperature 42 11,16 0,467*** 0,002691*** 0,311 Duration of main wash 81 43,71 0,452*** 0,001365*** 0,652 Constant = 0,812372
R = 0,907
R2 = 0,823
R2
Adjusted = 0,821 F= 302,661*** * p < 0,05 ** p < 0,01 ***p<0,001
Table 4-10: Collinearity statistics
Constant Tolerance VIF
Load size
0,552 1,811 Detergent
0,662 1,512
Actual washing temperature 0,942 1,062 Duration of the main wash 0,752 1,330
RESULTS 46
Tests to see if the data met the assumption of collinearity indicated that
multicollinearity is not a concern.
The histogram of standardized residuals indicated that the data contained
approximately normally distributed errors, as did the normal P-P plot of standardized
residuals, which showed points that were not completely on the line, but close.
The scatterplot of standardized residuals showed that the data met the assumptions of
homogeneity of variance and linearity. Based on the results of the multiple regression
analysis, the final equation to predict the amount of detergent is constructed.
The general regression equation (3-1), together with the variables selected by the
multiple linear regression analysis, is used to construct a model. The result is equation
(4-5).
𝑾 𝟎 𝟖𝟏𝟐𝟒 𝟎 𝟎𝟎𝟐𝟔 𝟎 𝟎𝟑𝟒𝟔 𝐋𝐎𝐀𝐃 𝟎 𝟎𝟎𝟏𝟐 𝐃 𝟎 𝟎𝟎𝟏𝟒 𝐃
(4-5)
As the equation is intended to be used to calculate the amount of detergent consumed
during a washing cycle, it is solved for detergent. The result is equation (4-6).
𝑾 𝟎 𝟖𝟏𝟐𝟒 𝟎 𝟎𝟎𝟐𝟔 𝑴 𝟎 𝟎𝟑𝟒𝟔 𝐋𝐎𝐀𝐃 𝟎 𝟎𝟎𝟏𝟒 𝐃
𝟎 𝟎𝟎𝟏𝟐 (4-6)
Where is:
WP p x TEMP p °C LOAD k DET MWD
RESULTS 47
4.3 Results of the virtual washing household modeling approach
The results of programming of the virtual washing household are presented by
showing the course of the laundry stock. All examples feature the laundry stock of 15
weeks. In all figures the lines are for visualization purposes only. For the ease of
understanding the following examples, the scenario as defined in 3.2.4.2 does not
apply and following simplified scenario is assumed.
Each week: 1 kg of 30 °C laundry is added to the stock
2 kg of 40 °C laundry is added to the stock
3 kg of 60 °C laundry is added to the stock
Loading factor: 30 °C washing cycle = 50 % of the rated capacity
40 °C washing cycle = 100 % of the rated capacity
60 °C washing cycle = 100 % of the rated capacity
Figure 4-10: Example of 30 °C laundry stock course in a 5 kg rated capacity machine when 1 kg of laundry is added to the stock every week
The results of dynamic simulation of a virtual washing household show the course of
the laundry stock of a household that uses a washing machine with the rated capacity
of 5 kg. Every week 1 kg of laundry is added to the stock. The washing cycle is
conducted when the laundry stock is 5 kg (Figure 4-10).
Week 0 5 10 15
0
2
4
6
8
10
Am
ount
of la
undry
in
kg
Washing cycles at 30°C
RESULTS 48
Figure 4-11: Laundry stock course with three different washing programs/temperatures in a 5 kg rated capacity washing machine when every week 1 kg, 2 kg and 3 kg of laundry are
added to the 30 °C, 40 °C and 60 °C laundry stock
In addition to the course of 30 °C laundry stock, the courses of 40 °C and 60 °C
laundry stock are presented. In the case of the 40 °C laundry stock course, every week
2 kg of laundry is added, and in the case of the 60 °C laundry stock course 3 kg of
laundry is added to the stock (Figure 4-11).
Figure 4-12: Impact of the loading factor (implemented in the case of 30 °C load) on the laundry stock course of three different washing programs/temperatures in a 5 kg rated
capacity washing machine when every week 1 kg, 2 kg and 3 kg of laundry are added to the 30 °C, 40 °C and 60 °C laundry stock.
0 5 10 150
2
4
6
8
10
Week
Am
ou
nt of
laundry
in k
g
Washing cycles at 30°C
Washing cycles at 40°C
Washing cycles at 60°C
0 5 10 150
2
4
6
8
10
Week
Am
ou
nt of
laundry
in k
g
Washing cycles at 30°C
Washing cycles at 40°C
Washing cycles at 60°C
RESULTS 49
In the case of 30 °C, the load factor of 0.5 is implemented, so that the washing
machine conducts a washing cycle when the laundry stock reaches at least 50 % of the
washing machine’s rated capacity. In the third week, the 30 °C laundry stock reaches 3
kg of which 2,5 kg are washed so that 0,5 kg were left. In fourth week, 1 kg of laundry
is added so that the total amount of laundry is 1,5 kg (Figure 4-12).
Figure 4-13: Impact of the maximal laundry waiting time (implemented in all three programs/temperatures) on the laundry stock course of three different washing
programs/temperatures in a 5 kg rated capacity washing machine when every week 1 kg, 2 kg and 3 kg of laundry are added to the 30 °C, 40 °C and 30 °C laundry stock.The impact is
visible in the reduction of the laundry stock in the third week.
Implementation of the maximal laundry waiting time in the simulation routine is
visible in the course of all three washing temperatures. The maximal laundry time is
set to “up-to-2-weeks”. In the second week, all three laundry stocks are reduced
(Figure 4-13).
0 5 10 150
2
4
6
8
10
Week
Am
ou
nt of
laundry
in k
g
Washing cycles at 30°C
Washing cycles at 40°C
Washing cycles at 60°C
RESULTS 50
4.4 Results of yearly simulations
4.4.1 Washing machine’s rated capacity versus household size
The results of the simulation of a yearly usage of the virtual washing machines with
the washing machine’s rated capacity (WMRC) of 5 kg, 8 kg, and 11 kg by the virtual
washing household are presented. Each data point in the chart shows how much CO2
equivalent is emitted when the washing machine is used by a household (of different
sizes) for one year. The lines are for visualization purposes only.
The following maximal laundry waiting time (MLWT) abbreviations are applied:
MLWT = 0 maximal laundry waiting time is “up to 1 week”
MLWT = 1 maximal laundry waiting time is “up to 2 weeks”
MLWT = 2 maximal laundry waiting time is “up to 3 weeks”
MLWT = 3 maximal laundry waiting time is “up to 4 weeks”
Figure 4-14: Comparison of emission of CO2 equivalents when MLWT = 0
0 1 2 3 4 5 6 70
50
100
150
200
Number of person in household
Em
issio
n o
f C
O2 e
quiv
ale
nts
in
kg
Rated capacity - 5 kg
Rated capacity - 8 kg
Rated capacity - 11 kg
RESULTS 51
When the maximal laundry waiting time is “up to 1 week”, the lowest CO2 equivalents
emission values are in the case of 1-person household:
Washing machine with 5 kg WMRC emits 51,4 kg of CO2 equivalents
Washing machine with 8 kg WMRC emits 62,3 kg of CO2 equivalents
Washing machine with 11 kg WMRC emits 82,5 kg of CO2
The highest values are in the case of 7-person household:
Washing machine with 5 kg WMRC emits 187,7 kg of CO2 equivalents
Washing machine with 8 kg WMRC emits 165,1 kg of CO2 equivalents
Washing machine with 11 kg WMRC emits 153,5 kg of CO2 equivalents
Slopes of washing machines with 8 kg and 11 kg rated capacity interchange in the case
of a 4-person household. The slopes of washing machines with 5 kg and 8 kg rated
capacity interchange between the household sizes of 2- and 3-persons.
Figure 4-15: Comparison of emission of CO2 equivalents when MLWT =1
When the maximal laundry waiting time is “up to 2 weeks”, the lowest values are in
the case of 1-person household:
Washing machine with 5 kg WMRC emits 51,4 kg of CO2 equivalents
Washing machine with 8 kg WMRC emits 62,3 kg of CO2 equivalents
0 1 2 3 4 5 6 70
50
100
150
200
Number of person in household
Em
issio
n o
f C
O2 e
quiv
ale
nts
in
kg
Rated capacity - 5 kg
Rated capacity - 8 kg
Rated capacity - 11 kg
RESULTS 52
Washing machine with 11 kg WMRC emits 82,5 kg of CO2 equivalents
The highest values are in the case of 7-person household
Washing machine with 5 kg WMRC emits 187,7 kg of CO2 equivalents
Washing machine with 8 kg WMRC emits 165,1 kg of CO2 equivalents
Washing machine with 11 kg WMRC emits 153,5 kg of CO2 equivalents
Slopes interchange at 2-person household tick mark.
Figure 4-16: Comparison of emission of CO2 equivalents when MLWT =2
When the maximal laundry waiting time is “up to 3 weeks”, the slope of the washing
machine with a rated capacity of 8 kg and 5 kg have the lowest CO2 equivalents
emission values for a 1-person household with 27 kg (WMRC = 8 kg) and 27,6 kg
(WMRC = 5 kg). The highest CO2 equivalents emission is in the case of the washing
machine with a 5 kg rated capacity (189,7 kg). The interchange of the slope course is
at the 1-person household tick mark.
0 1 2 3 4 5 6 70
50
100
150
200
Number of person in household
Em
issio
n o
f C
O2 e
quiv
ale
nts
in k
g
Rated capacity - 5 kg
Rated capacity - 8 kg
Rated capacity - 11 kg
RESULTS 53
Figure 4-17: Comparison of emission of CO2 equivalents when MLWT = 3
When the maximal laundry waiting time is “up to 4 weeks”, the lowest values of CO2
emission are in the case of the washing machine with a rated capacity of 8 kg and a
1-person household with 24,8 kg of CO2 equivalents emitted. The highest values of
CO2 equivalents emission are in the case of the washing machine with a rated load
capacity of 5 kg with 189,7 kg in the case of a 7-person household.
0 1 2 3 4 5 6 70
50
100
150
200
Number of person in household
Em
issio
n o
f C
O2 e
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in k
gRated capacity - 5 kg
Rated capacity - 8 kg
Rated capacity - 11 kg
0 2 4 6 0
50
100
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200
Em
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O2
equ
iva
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ts in
kg
5 kg
0 2 4 6 0
50
100
150
200 8 kg
0 2 4 6 0
50
100
150
200
Number of persons in household
11 kg
RESULTS 54
Figure 4-18: Overview of washing machine’s rated capacity vs. MLWT
An overview of all washing machines in dependence of the maximal laundry waiting
time show a strong gap between the slopes of the curves as the loading capacity of the
washing machine increases.
RESULTS 55
4.4.2 CO2 equivalent emission of water detergent and energy
Figure 4-19: CO2 equivalents emission split by individual resource consumption share
where MLWT = 0 (4-19a) and MLWT = 3 (4-19b). Each of the seven columns within each rating capacity class represents household ranging from 1-person households (First column)
to 7-person households (Seventh column).
CO2 equivalents emission is split by the individual share of the resources consumed.
The share of the energy and detergent in the total CO2 equivalent emission are the
highest. The share of the CO2 emission for water is minimal.
5kg 8kg 11kg0
50
100
150
200
Washing machine rated capacity
Em
issio
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O2 e
quiv
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5kg 8kg 11kg0
50
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Washing machine rated capacity
Em
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a b
RESULTS 56
4.4.3 Comparison of the time exposure4
Figure 4-20: Time exposure in dependence of the rated capacity, household size and MLWT (Starting with maximal laundry waiting time of “up to 1 week” (Chart a) to maximal laundry
waiting time of “up to 4 weeks” (Chart d)).
Time exposure depends on the maximal laundry waiting time, washing machine’s
rated capacity and the number of persons in the household. Figures a-d show the time
exposure in dependence of the maximal laundry waiting time. The time exposure is the
highest when the maximal laundry waiting time is the lowest. With an increase of the
4 Time consumed for washing (expressed in number of washing cycles). It is composed of the regular washing
cycles (cycles where the rated capacity of the washing machine is used) and emergency washing cycles (cycles
where the washing machine’s rated capacity is not used due to reaching the maximal laundry waiting time).
1 2 3 4 5 6 70
100
200
300
400
Number of Person in household
Num
be
r of w
ashin
g c
ycle
s
Regular washing cycles
Emergency washing cycles
1 2 3 4 5 6 70
100
200
300
400
Number of Person in householdN
um
be
r of w
ashin
g c
ycle
s
Regular washing cycles
Emergency washing cycles
1 2 3 4 5 6 70
100
200
300
400
Number of Person in household
Num
be
r of w
ashin
g c
ycle
s
Regular washing cycles
Emergency washing cycles
1 2 3 4 5 6 70
100
200
300
400
Number of Person in household
Num
be
r of w
ashin
g c
ycle
s
Regular washing cycles
Emergency washing cycles
a b
c d
RESULTS 57
maximal laundry waiting time, the total time exposure as well as the share of the
emergency washing cycles decreases.
4.4.4 Comparison of average washing temperatures5
Figure 4-21: Comparison of average washing temperatures in dependence of the household size: 1-person household (4-21a) – 4-person household (4-21d)
5 Arithmetically-averaged washing temperature of all washing cycles conducted during one year
5kg 8kg 11kg30
35
40
45
Washing machine rated capacity
Ave
rage te
mp
era
ture
in °
C
1 Person (MLWT = 0)
1 Person (MLWT = 1)
1 Person (MLWT = 2)
1 Person (MLWT = 3)
5kg 8kg 11kg30
35
40
45
Washing machine rated capacity
Ave
rage te
mp
era
ture
in °
C
2 Person (MLWT = 0)
2 Person (MLWT = 1)
2 Person (MLWT = 2)
2 Person (MLWT = 3)
5kg 8kg 11kg30
35
40
45
Washing machine rated capacity
Ave
rage te
mp
era
ture
in °
C
3 Person (MLWT = 0)
3 Person (MLWT = 1)
3 Person (MLWT = 2)
3 Person (MLWT = 3)
5kg 8kg 11kg30
35
40
45
Washing machine rated capacity
Ave
rage te
mp
era
ture
in °
C
4 Person (MLWT = 0)
4 Person (MLWT = 1)
4 Person (MLWT = 2)
4 Person (MLWT = 3)
a b
c d
RESULTS 58
With an increase of the maximal laundry waiting time, the average washing
temperature decreases. The values are the lowest when the maximal laundry waiting
time is “up to 4 weeks” (40 °C e.g. 2-person household). The highest values are in the
case when the maximal laundry waiting time is “up to 1 week” (43 °C in e.g. 1-person
household).
DISCUSSION 59
5 Discussion
5.1 Virtual washing machine
The first goal of this study was to develop a model of a virtual washing machine that is
based on the data of washing machines available on the market. Although three
equations are necessary to describe the washing process, it can be concluded that the
goal of a construction of a virtual washing machine is reached.
The fact that three equations are necessary to describe the washing machine process is
due to its complexity. On one hand, there are numerous variables that impact the
process, and on the other hand there are three dependent variables where each has to
be calculated by using a separate predicting model. In the following, the individual
equations are discussed.
5.1.1 Equation for calculation of water consumption
The function of water in the washing process is manifold. It is not only the medium
that transports the detergent and heat to the fabric surface and facilitates the removal of
the soil, but it is also the medium where the soil is stabilized so that a redeposition is
prevented. (JAKOBI and LÖHR, 1987)
Since 1970, numerous inventions have led to a decrease of the water consumption.
Average water consumption of 200 liters in 1970 (STAMMINGER et al., 2005) decreased
to today’s consumption of 42,6 liters (VHK, 2013).
The data of the washing machine’s tests (Figure 4-1 and Figure 4-2) and the resulting
equation show that load size and rated capacity are the two most influential factors on
the water consumption of a washing machine.
However, data also reveals that there are many variations among washing machines in
their ability to adapt the water consumption to the load, especially when they are not
fully loaded. In some cases, the specific water consumption for washing nearly same
DISCUSSION 60
amount of load can vary up to double the amount when the washing machine is
underloaded (Figure 4-2).
As the washing machines test data shows, the differences among washing machines’
abilities to adapt the water consumption to the load is lowest when the washing
machine is fully loaded. This is confirmed also by (RÜDENAUER et al., 2004), who also
found out that with a decrease of the load size, the specific consumption of the water
and energy increases.
The consumers, however, do not fully load their washing machine. They consider, for
example, a load of 3,7 kg to be a full load in a washing machine which has a rated
capacity of 5 kg (KRUSCHWITZ et al., 2014). In order to lower the resource
consumption, most of today’s washing machines are equipped with sensors that
control the washing machine and automatically adapt the resource consumption to the
load. With a decrease of the load size, the water consumption decreases.
(WAGNER, 2011)
As data shows, this is not always the case.
The fact that fully loaded washing machines show the lowest variance in the water
consumption might be viewed as a direct consequence of the energy label standard
EN60456:2005, which was in force when the tested washing machines were produced.
The standard stipulated that washing machines are to be tested with a full load when
tested according to the energy label. There was no incentive for the manufacturers of
white goods to optimize the washing machines to anything other than full-load size.
The reason for variations in the water consumption when the washing machine is not
fully loaded, however, might be because of the accuracy of the sensor and fuzzy logic
implemented. It is possible that the sensors do not react precisely, and therefore
influence the fuzzy inference so that variations in water consumption occur.
The data shows that the washing machine’s rated capacity influences the water
consumption as well. Washing machines with a higher rated capacity have higher
absolute water consumption; however, with an increase of the load size, the specific
DISCUSSION 61
water consumption decreases. A possible reason for this is that washing machines let
in some amount of water, whether it is loaded or not. This minimal amount of water is
needed for the protection of the washing machine namely some of its components,
such as the heater, which might suffer damage when preheating and running without
water that would absorb the heat. In washing machines with a higher rated capacity,
this minimal amount has a lower impact on the specific water consumption than in the
case of washing machines with a lower rated capacity.
5.1.2 Total water consumption
Total water consumption depends mainly on the number of rinsing cycles (WAGNER,
2011). The number of the rinsing cycles again depends on what the manufacturer
wants to offer to its consumers as a standard program.
In some cases, the consumers are offered a washing program with a lower number of
rinsing cycles as a standard, and the consumers have to use additional options such as
“water plus” or “extra rinsing” in order to receive a higher rinsing performance.
Alternatively, some manufacturers offer the consumers a washing program with a
higher water consumption, i.e. with more rinsing cycles as a standard washing
program and it is up to the consumers to include the water-saving options, such as
“economy wash” or “half load” in order to save water.
In some cases, even the sensors that monitor the washing process can influence the
water consumption. For example, the number of rinsing cycles can vary depending on
the quality of the foam detection sensors.
A look into the comparison of the average values of total water consumption to main
wash water consumption reveals that this ratio is 1:3,5 no matter whether the detergent
dosage is nominal, under- or overdosed. Assumption that the fuzzy logic would adapt
to the water consumption if the amount of detergent is overdosed is not met.
A possible explanation for this might be because of the detergent used for washing
tests. In this case, the EN60456:2005 standard detergent A* is used, where the amount
DISCUSSION 62
of foam inhibitor is very high. For this reason it is possible that the foaming detection
sensors recognize that no further rinsing cycles are induced.
Another reason for this might be because of the washing program design of the tested
washing machines. It might be possible that the number of the rinsing cycles is not
sensor/fuzzy logic controlled and a standard number of rinsing cycles is included in
the washing process.
Energy consumption
In a washing machine, energy is consumed for heating the water, running the main
motor and the drain pump, as well as for running the sensors, control processor and
other electronic signaling units of the washing machine. During the washing machine’s
test, the energy consumption of the processor and signaling unit were not measured.
About 91,9 % in the variation in energy consumption can be explained by independent
variables: actual washing temperature, water consumption, and the duration of the
main wash. This coefficient of determination value can be considered to be good when
the afore-mentioned variances among different washing machines are taken into
account.
The most energy, however, is consumed for electrically heating up the water,
especially when the inlet water is not preheated (KUTSCH et al., 1997; SMULDERS,
2007; WAGNER, 2011). This is also confirmed by the data received in the washing
machine’s test. With an increase of the temperature, the energy consumption increases.
The higher the washing temperature, the more energy is needed to heat up the water,
hence more energy is consumed. (SMULDERS et al., 2007)
The data, however, shows differences in energy consumption among different washing
machines and different load sizes. Since the water consumption strongly depends on
load size, the energy consumption indirectly also depends on the load size, so that the
dependencies discussed in 5.1.1 also apply here.
DISCUSSION 63
Furthermore, the data shows that some washing machines do not always heat up the
water to the preset temperature (Table 4-5). For example, WM9 reaches, in a nominal
60 °C program, a maximal actual washing temperature of 47 °C.
The reason for this might be in the specification given in the Eco-design regulation.
According to it, the washing machines have to reach a certain washing performance
index. In a reference 60 °C program, a washing index of 1,03 is required. In practice
this means that the manufacturers have to provide one program for each washing
machine that fulfills those conditions, and this program is to be used when the washing
machine is tested. It is up to the manufacturer to find a perfect combination of the
washing factors so that the required washing performance can be achieved. In order to
save energy, some washing machine producers lower the actual washing temperature
and increase the main washing time. VAN HOLSTEIJN EN KEMNA, 2013 also observed this
trend of prolonging the washing cycle in washing machines, which “opens the
possibility to wash with lower temperatures with the same washing result and can
therefore increase the energy efficiency.” (VHK, 2013, p.41) They see a risk in those
longer cycle times, in such that “people might not use the energy efficient program but
will use the normal cotton program instead. They might simply not have the time to
wait for 5 hours before they can start the next load.” (VHK, 2013, p.41)
Due to this discrepancy between the nominal washing temperature and the actual
washing temperature, in the energy equations the maximally reached actual washing
temperature is included. With beta values of 0,72 (Table 3-1), the washing
temperature’s contribution to the explanation of the variance is the highest. The
contribution of the duration of the main wash is roughly as high as the contribution of
the water consumption to the explanation of the variance.
Analogous to the water consumption, the real energy consumption also depends on
what the manufacturer wants to offer to the consumer as a standard washing program.
In some cases, the manufacturer offers a shorter program as standard and the consumer
has to use the “intense” or “stains” option to extend the program. Other manufacturers
DISCUSSION 64
offer a longer washing program as a standard program, and the consumer has to
choose the “express” or “short” option in order to shorten the washing program.
However, under certain circumstances, even the duration of the main wash has more
influence on the energy consumption than the chosen temperature. In those cases
when a low washing temperature and long duration of the main wash is selected
(which are, for example, the case in an eco-program), the share of the energy
consumed for heating up the water is lower than the share of energy consumed by the
engine.
In the equation eq. (4-4), the constant (y-intercept) is -0,836 kWh. Assuming that all
the explanatory variables are set to 0, the value of the response variable would be
negative. However, as seen in the equation for the calculation of water consumption,
4,01 L of water is always consumed, and its temperature is higher than 0 °C in order to
be even in fluid state and hence added to the washing machine. For this reason the
validity of the equation is limited.
5.1.3 Detergent consumption
The equation for calculating the detergent consumption is based on a multiple
regression that sets the washing performance in relation with the load size, duration of
the main wash, actual washing temperature and amount of detergent. The final
equation is then developed by solving the equation for detergent.
Consumer behavior influences the outcome of a washing cycle. In a washing cycle, the
consumer has to decide (1) how much of laundry to load, (2) what washing program
(temperature, duration, spinning speed, rinsing characteristics) to choose, and (3) what
kind of detergent to use and how much to dose. In the equation, some of those
consumer patterns are included, and each can be adjusted separately.
The washing machine test data shows that the load size has a strong impact on the
washing performance (Figure 4-6). The beta values of the multiple regression analysis
(Table 4-9) show that the load size actually has the highest impact on the washing
DISCUSSION 65
performance index of all variables. A negative B value of the load (-0,034584)
indicates that every ceteris paribus increase of the load size results in a decrease of the
washing performance index.
In accordance with SINNER 1961, with a lower load size the free space in the drum
increases and hence the laundry has more space to tumble down, increasing the
mechanical force. When all other factors are kept constant, an increase of the washing
performance index occurs.
The virtual washing machine offers a set of input parameters (e.g. load amount,
washing temperature, etc.), in which each can be individually varied. Only those
variables that can actually be chosen by the consumer are included in the model. A
washing program can be simulated by combining/varying those parameters.
- Temperature: Washing temperatures between 30 °C and 60 °C can be preset in
the equation. As previously discussed in chapter 5.1.2, there is a discrepancy
between the nominal and actual washing temperature.
- Duration of the main wash: In real-life washing machines, there is not a
possibility to preset the duration of the main wash in the same manner as is
possible with the washing temperature or the spin. However, with time
consumers learn which washing programs are short and which are long, and
choose the respective program when needed. By doing so, consumers are able
to influence the duration of the washing program. Another possibility to
influence the duration of the main wash is by choosing other options, such as
the “short” or “intense” option.
There are also some limitations of this “virtual program” in comparison to the real-life
washing programs. For example, some washing programs interrupt the main wash
program with spinning cycles in order to facilitate the wetting process. However, in
this virtual washing machine those specific program designs are not implemented.
The data shows that with a decrease of the average washing temperature, the washing
performance index decreases. This fact also shows that there is a potential for tradeoff
DISCUSSION 66
between the washing temperature and the washing performance. Furthermore, there is
also interdependency between the washing performance and the amount of detergent
(Figure 4-8). This bears a potential for a tradeoff for consumers who have to wash
textiles for which a lower washing performance is acceptable (e.g. slightly soiled
textiles). In those cases, where there is no need to have a high washing performance,
consumers can lower the washing temperature and thus save energy. Alternatively for
the consumer, there is a possibility to lower the amount of detergent.
5.2 Virtual washing household
The second goal of the present work is to develop a model of a household washing
behavior that incorporates the household- and behavioral parameters.
The mathematical model presented in 3.2.3 differs from models presented by other
research because it does not calculate with a fixed load size, but rather varies during
the simulation in accordance with model settings. Furthermore, it allows a variation of
certain parameters such as: number of persons in household, amount of load per
person, and shares of different program/temperature batches of the total amount of
load.
An important variable in the model of the virtual washing household is the loading
factor (Figure 4-12).
Most of the mathematical models presented by other researchers are very simple, and
in most cases the calculations are done by assuming the consumer uses a full load (or
possibly a half load). A loading factor, which depends on the type of laundry, is not
included in such calculations.
The consumers, however, do not use the full capacity of the washing machine.
According to STAMMINGER, 2011, 10 % of consumers in Europe load the washing
machine in dependence of the type of laundry, and 63 % load the washing machine
without overloading it. Consumer associations also promote fully loading the washing
machine, except when washing delicates, in which case a half load is recommended
(ForumWaschen, 2013). By using the virtual washing household model, it is possible
DISCUSSION 67
to include all different loading factors that differ in dependence of the type of laundry
that has to be washed.
The key moderating parameter in this simulation design is the maximal laundry
waiting time parameter (Figure 4-13).
With this variable, it is possible to add a time dimension to the virtual washing
household model and so explore the effects that might occur when the consumer is
ready to postpone an action (in this case the washing of laundry) to a later point of
time. For example, “being in hurry” can be simulated by shortening the MLWT and
“environmentally conscious” behavior can be simulated by extending the maximal
laundry waiting time.
In this work, it is possible to simulate the usage of a washing machine, in a parallel
manner, by households of different sizes. Comparison of the usage of the same
washing machine by households (of up to seven persons) helps to reveal how the
household size influences the consumption.
5.3 Simulations
The third goal of the present work is to develop and conduct simulation of the usage of
the virtual washing machine by the virtual washing households. By conducting parallel
simulations and by varying device-, household- and behavioral parameters, a
parameter combination with the lowest environmental impact can be determined, and
hence conclusions regarding an optimal consumer behavior can be drawn. In order to
answer this question, the following aspects are examined:
- Washing machine’s rated capacity
- Resource consumption
- Washing frequency
- Average washing temperature
DISCUSSION 68
5.3.1 Washing machine’s rated capacity
Environmental impact of automatic washing depends not only on the household size
and the washing behavior (i.e. maximal laundry waiting time), but also the washing
machine’s rated capacity.
Comparison of the slopes in Figure 4-14 shows that when the maximal laundry waiting
time is very low, households with a lower number of persons would have the lowest
impact on the environment when using a washing machine with a lower rated capacity.
A washing machine of 8 kg or even 11 kg would be less adequate in such a case.
With an increase of the number of persons in the household, a washing machine with a
higher rated capacity becomes more adequate. With an increase of the maximal
laundry waiting time, the amount of laundry that accumulates in a household increases
further. In such a case, a washing machine with a higher rated capacity becomes more
adequate due to use of the economies of scale potential of such washing machines
(Figure 4-15 - Figure 4-17).
A usage of washing machines with a higher rated capacity by smaller households (for
example 1-3 person households) demands change of the behavioral patterns. One
possibility is that the household increases the maximal laundry waiting time and waits
until enough laundry is accumulated so that the rated capacity of the washing machine
can be used. However, it is questionable whether the consumers are willing to wait for
three or more weeks until enough laundry is accumulated.
Another possibility for more sustainable usage might be in combining the different
washing loads. For example, by combining a 30 °C and 40 °C washing load, and by
choosing the washing temperature in accordance with the recommendation of the most
sensitive laundry piece, and in combination with prolonging the washing cycle, the
same washing performance at a lower resource consumption may be achieved.
(JUNGBLUTH et al., 2006) as well as (JANCZAK et al., 2010) have already shown that
lowering the temperature to the next possible level and prolonging the washing time
leads to a decrease in the energy consumption while the washing performance remains
the same.
DISCUSSION 69
It should also be kept in mind that a continuous usage of lower temperatures may
generate some other issues, such as problems with hygiene. In such cases, the usage of
appropriate washing detergent, such as a bleach-containing detergent, could help to
resolve those issues. Furthermore, in this respect, the consumer should consider
following the suggestions of the consumer association to cyclically wash at higher
temperatures, and to leave the door and the detergent container open after a washing
cycle.
5.3.2 Resource consumption
The resource consumption comparison shows that energy and detergent have the
highest share in CO2 emission. The share of the water is not very high. The reason for
this is that the water consumption has been optimized in the past decades. According
to the EuP preparatory study, water consumption has reduced from 1997 to 2005, with
an annual improvement of 0,28 l / kg (PRESUTTO et al., 2007).
The contribution of the energy to the total CO2 emission is highest when a smaller
household uses a washing machine with a higher rated capacity and the maximal
laundry waiting time is very short. In such a case, the household never uses the rated
capacity of the washing machine as shown in the model. With a lower amount of load,
the mechanical work is increased (SINNER, 1961) and therefore a lower detergent
dosage is needed to reach the preset washing performance. In such cases, the energy
related CO2 equivalent emission is more than three times higher than the CO2
equivalent emission of detergent (Figure 4-19).
For the calculations of the energy consumption, it was assumed that an energy mix is
used, where a certain portion is produced using nuclear-, coal- and renewable energy
sources. In this case, the CO2 equivalent conversion factor for energy is 600 g / kWh.
In an energy mix with a lower CO2 equivalent emission (which might come in the
future), the detergent consumption might have a higher influence on the CO2 emission
than the energy consumption.
DISCUSSION 70
On the other hand, it is also possible that more advanced technology in detergent
production might occur, which then could lead towards a lower impact of the detergent
on the CO2 equivalent emission.
In both cases, there is a potential for tradeoff between the energy and the detergent that
could be used in order to have an even more sustainable behavior.
5.3.3 Washing frequency
The time consumed for washing purposes is also an important factor when evaluating
the different washing behavior patterns. Although the time consumed for washing
purposes includes the washing machine loading/unloading time as well as the washing
time, in this research the washing frequency solely represents time consumption.
One of the arguments for selling washing machines with a large load capacity is that it
is time saving, since more loads can be washed at the same time, hence the consumers
are able to reduce the number of washing cycles when using those washing machines.
However, this depends on the household size and the washing machine’s rated
capacity, as well as on the consumer behavior when using the washing machine.
As presented in the data (Figure 4-20), two different washing cycles are to be
distinguished. The first one is a “normal washing cycle”, in which the washing
machine’s rated capacity (adjusted for the load factor) is fully utilized. The second one
is an “emergency washing cycle”, in which the washing cycle is conducted no matter
how much laundry is loaded.
The behavioral factor that influences the frequency of emergency washing cycles is the
maximal laundry waiting time. For example, when the maximal laundry waiting time
is “up to 7 days” there is almost no difference if consumers use 5 kg, 8 kg or even
11 kg washing machine in cases of one-person and two-person households. In all those
cases, the washing machine’s rated capacity is not fully used, which means that most
of the washing cycles are “emergency washing cycles” and hence no time is saved.
DISCUSSION 71
With an increase of the household size, the number of emergency washing cycles
decreases, and the differences among washing machines regarding the washing
frequency becomes more visible.
An exception is the 11 kg washing machine, in which the emergency washing cycles
also occur in the case of a 7-person household, when the maximal laundry waiting
time is low. The reason for this is that even a 7-person household does not have
enough 60 °C laundry which can be collected in such a short time in order to use the
rated capacity of the washing machine. However, with an increase of the maximal
laundry waiting time, the number of emergency washing cycles decreases here as well.
The consequences of the washing frequency are manifold:
- Firstly, high usage frequency might be stressful for the consumer. For example,
those consumers whose work life allows washing only on weekends, or
consumers who use a community washing machine, might experience the high
washing frequency as very tedious. It is possible that in such cases those
consumers, in order to be able to wash more washing cycles in a shorter period
of time, chose to use a shorter washing program that might be inadequate from
the resource consumption, hygienic or/and general cleanliness perspective.
- Secondly, with an increased frequency, a fatigue of material in the washing
machine, such as the drum casing bumpers, could undergo damage, as well as a
lower life expectancy of the washing machine. ÖKO-INSTITUT calculates that a
washing machine can be used for 1840 washing cycles (RÜDENAUER et al., 2004).
A non-optimal usage might shorten the life expectancy of a washing machine.
5.3.4 Average washing temperature
Data received from the washing machine test and the eq. (4 4) show that the energy is
directly correlated with the chosen washing temperature. In order to lower energy
consumption, washing at lower temperatures is promoted. Since the early 1970s, the
DISCUSSION 72
average washing temperatures have declined. This is a good indicator for the
promotion of a more environmentally friendly behavior (AISE, 2013).
As the data shows (Figure 4-21), the influence of the maximal laundry waiting time on
the average washing temperature is also highly important. With an increase of the
laundry waiting time, the rated capacity of the washing machine is used more often
(which is especially the case of the 60 °C washing cycles, in which the loading factor
is highest), and hence the average washing temperature decreases. This finding is of
high importance for two reasons:
Firstly, consumer associations’ promotion of lower temperatures has often encountered
a resistance among consumers, due to probable perceived washing performance
inefficiency. A possible solution to this problem might be in promoting the extension
of the maximal laundry waiting time, which then would induce the use of the washing
machine’s rated capacity, and therefore might lead to a decrease of the average
washing temperature.
Secondly, those consumers who do not wish to decrease the washing temperature due
to fear of hygiene-related issues can, at least to some extent, contribute to
environmental protection by increasing the maximal laundry waiting time and so lower
the household average washing temperature.
Furthermore, the data shows that the effects of decreasing the average washing
temperature while increasing the maximal laundry waiting time occur in dependence
of the washing machine size and the household size.
For example, a washing machine with a 5 kg rated capacity used by a 1-person
household has a potential to lower the average washing temperature when increasing
the maximal laundry waiting time. However, usage of an 11 kg washing machine by a
1-person household does not bear such a potential.
It can be concluded that there is an optimal washing machine’s rated capacity for each
household size.
DISCUSSION 73
5.4 Deficits of the presented research
Although the virtual washing machine and the virtual washing household display a
robust predicting power, there are still some aspects which should be critically
observed.
In the present work, the hygiene and the soil re-deposition were not a subject of
research. However, those aspects should also be considered, because the hygiene
aspect in laundry washing, as well as the soil re-deposition, is increasing, which is
something the consumers are able to evaluate at the end of a washing cycle. This could
induce a behavioral change towards rewashing the laundry, or usage of less resource-
saving programs, such as intense or water plus programs.
The duration of the main wash in the virtual washing machine model is automatically
selected in dependence of the washing machines’ rated capacity. The values used are
average values of the individual washing machines groups. Such an approach is
certainly valid in order to predict the resource consumption of tested washing
machines. However, generalizing all washing machines should be used with caution.
In the virtual washing machine, the rinsing cycles are not part of the model and a
constant factor is included instead. Such a simplified approach allows for an
estimation of the resource consumption, but the model does not allow the inclusion of
consumer behavior in usage of rinsing options (water plus option or sensitive option).
An inclusion of the rinsing cycles in the model would enhance the model and make it
more precise in predicting the water consumption.
The virtual washing machine model allows for the prediction of energy consumed
during the main wash. However, although the share of energy consumed during the
rinsing phase and spinning phase, as well as in the standby mode, is not as high as the
energy consumed during the main wash, its inclusion in the virtual washing machine
model would allow a more precise prediction of the resource consumption.
Detergent used for the washing machine test is A* detergent as specified by
EN60456:2005. Usage of A* detergent helps to compare the washing machines.
Commercially available detergents used by consumers, however, differ significantly.
DISCUSSION 74
Commercial detergents contain advanced components (e.g. enzymes) that allow lower
dose amounts without lowering the washing performance. Inclusion of the commercial
detergent in the model would provide an even more precise picture of the influence of
washing on the environment.
In the case of the virtual washing household, it was assumed that the household
displays an ideal behavior when washing laundry. However, this is not the case in real
life. Such an approach only helps to illustrate the real-life behavior to some extent.
There are many parameters that influence the consumer behavior such as the gender
age of the participants or even seasonal aspects which are not included in this research.
An inclusion of those aspects would help to explore the consumer behavior more
thoroughly.
CONCLUSION AND FUTURE PROSPECTS 75
6 Conclusion
Based on the data of different washing machines, a model of a virtual washing
machine was developed and, despite the large differences among the tested washing
machines, it shows a robust predicting power.
The developed virtual washing household model offers a high range of possibility to
simulate some of the consumers’ behavioral patterns. Its dynamic development of the
laundry stock course and possibility to vary household and washing machine
parameters makes this model more advanced in comparison to the modeling solutions
described in the literature.
The virtual washing household model, used in this work, could also be used to
simulate usage of other household appliances. For example, the virtual washing
household model could also be used to simulate the usage of automatic dishwashers or
tumble dryers. By extending the model to more household appliances, a more precise
resource consumption-predicting model could be established and used to predict the
daily energy consumption and possible peak demands. Furthermore, it would enable a
simulation of more precise trend developments so the policy making decision could be
supported.
In connection with this, the variable maximal laundry waiting time has proven to be of
great help in adding a “sustainability component” to the consumer model. At present,
no research has evidenced the usage of such a moderating factor that has been
presented in the literature. The maximal laundry waiting time parameter is of great
value due to its ease of use and its ability to support the increasing value of
information that must retrieved in behavior-related simulations. Furthermore, it
reflects real-life behavior very well, in cases where consumers do not wash the same
amount of laundry every week, but instead only wash when there is enough laundry or
when certain loads have to be washed, regardless of whether the rated capacity is fully
used or not (emergency washing cycle). For this reason, it should be included as an
CONCLUSION AND FUTURE PROSPECTS 76
eventual standard variable in future models where the sustainability-related consumer
behavior is being explored.
CONCLUSION AND FUTURE PROSPECTS 77
7 Future prospects
In the present study, the amount of laundry added to the washing machine, as well as
the rated capacity of the washing machine are each expressed in kilograms. However,
in some cases the declared increase of the washing machine’s rating capacity is not
followed by a volume increase of the washing machine’s drum. In such cases, the
resulting overload of the drum and consequent decrease of mechanical work (Sinner,
1960) is substituted by an increase of the other washing factors, such as the washing
time.
For this reason, in a follow-up model of the virtual washing machine, it would be
important to include the washing machines’ drum volume instead of the rated capacity
expressed in kilograms.
Furthermore, in the following study the actual washing temperature is measured in the
sump (that is, in the space in-between the inner and outer drum at the bottom of the
washing machine’s drum). This temperature is not necessarily the same as the
temperature in the load (especially at the spot where textile, soil and wash liquor
meet). However, the temperature at this spot is actually influencing the washing
performance. An inclusion of this parameter in a future follow-up virtual washing
machine model should be considered so that it might lead to a more accurate model.
In addition, for the washing machines’ tests, cotton was used as a test load. In an
eventual follow-up model, other fabrics such as synthetics should also be included as
test loads. This would allow for a more realistic, real-life relevant model. Additionally,
in the follow-up model other detergents (liquor detergent, commercial detergent, etc.)
and new washing machines models (e.g. models that use heat-pump and/or automatic
dosing) should be included.
The virtual washing household model also bears potential for improvement. In the
presented study it was assumed that the consumer washes every temperature-specific
load separately. In real life, however, this is not the case and the consumers often
combine two (temperature/program) batches of laundry together. A possible
CONCLUSION AND FUTURE PROSPECTS 78
optimization of the model should also include such behavioral patterns in the
simulation.
Furthermore, additional research is necessary to identify the driving forces of non-
optimal consumer behavior (e.g. lack of time, habit to wash every week, convenience
of always having clean laundry or to wash on specific weekdays). The findings of such
research could, together with findings of this study, be used to develop practicable
tools that stimulate more sustainable behavior. Such tools could be used to promote the
increase of the maximal laundry waiting time. For example:
Consumer associations could develop an info brochure informing
consumers to separate the laundry not only by the color/soil level or type
of textile, but to also include a “washing priority” category.
Consumer associations could develop advising tools (e.g. checklist)
which could be used as guidance when buying a new washing machine.
Industries could develop information systems on the washing machine
that promotes the extension of the maximal laundry waiting time (e.g.
washing frequency tracker, sticker/dosing ball that changes color when
used too frequently.
Detergent manufacturers could develop products that encourage a longer
usage of textiles.
REFERENCES 79
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ABBREVIATIONS 85
9 Abbreviations
°C Degree celsius
ca. circa
e.g. exempli gratia
et al. et alteri
g Gramm
h Hour
Hz Hertz
i.e. Id est
kg Kilogram
kWh Kilowatt-hour
L Liter
mg Milligramm
min Minute
MLWT Maximal laundry waiting time
mmol / L Millimol per liter
p. Page
resp. Respectively
s Second
V Volt
W Watt
WM Washing machine
WMRC Washing machine rated capacity
Arithmetic mean
ABBREVIATIONS 86
FIGURES 87
10 List of figures
Figure 1-1: Sinner’s circle (own representation)...................................................................... 1
Figure 1-2: Sinner's circle for washing by hand (own representation) ..................................... 2
Figure 1-3: Sinner's circle for washing in a washing machine at a high temperature
(own representation) .......................................................................................... 2
Figure 1-4: Average load capacity trends of household washing machines ............................ 7
Figure 1-5: Life cycle analysis of a washing machine (Source: RÜDENAUER et al.) .................. 9
Figure 1-6: Contribution of the different sectors to the GHG emission
(Source: EEA, 2010) ........................................................................................ 13
Figure 3-1: Example of a testing procedure on an example of a 25 % load .......................... 23
Figure 3-2: Schematic of the mathematical model construction of a washing
machine (own representation) .......................................................................... 28
Figure 3-3: Example of a schematic of the simulation ........................................................... 29
Figure 4-1: Water consumption versus load of nine washing machines - washing
temperature is 60 °C ........................................................................................ 33
Figure 4-2: Comparison between the specific water consumption and the load size ............. 34
Figure 4-3: Water consumption versus load amount - washing temperature is 60 °C ........... 34
Figure 4-4: Energy consumption in kWh versus load size. Washing temperature
60 °C ............................................................................................................... 36
Figure 4-5: Energy consumption versus load amount - washing temperature is 60 °C ......... 36
Figure 4-6: Index of washing performance versus load for cotton 60 °C ............................... 37
Figure 4-7: Index of washing performance vs. energy consumption. From left to right
the energy values indicate the machines' energy use for 30 °C, 40 °C
and 60 °C washing programs ........................................................................... 38
FIGURES 88
Figure 4-8: Index of washing performance vs. detergent dosage .......................................... 39
Figure 4-9: Schematic of a construction of a virtual washing machine based on the
data received during the washing machine tests .............................................. 41
Figure 4-10: Example of 30 °C laundry stock course in a 5 kg rated capacity
machine when 1 kg of laundry is added to the stock every week ..................... 47
Figure 4-11: Laundry stock course with three different washing
programs/temperatures in a 5 kg rated capacity washing machine
when every week 1 kg, 2 kg and 3 kg of laundry are added to the 30
°C, 40 °C and 60 °C laundry stock ................................................................... 48
Figure 4-12: Impact of the loading factor (implemented in the case of 30 °C load) on
the laundry stock course of three different washing
programs/temperatures in a 5 kg rated capacity washing machine
when every week 1 kg, 2 kg and 3 kg of laundry are added to the 30
°C, 40 °C and 60 °C laundry stock. .................................................................. 48
Figure 4-13: Impact of the maximal laundry waiting time (implemented in all three
programs/temperatures) on the laundry stock course of three different
washing programs/temperatures in a 5 kg rated capacity washing
machine when every week 1 kg, 2 kg and 3 kg of laundry are added to
the 30 °C, 40 °C and 30 °C laundry stock.The impact is visible in the
reduction of the laundry stock in the third week. ............................................... 49
Figure 4-14: Comparison of emission of CO2 equivalents when MLWT = 0 .......................... 50
Figure 4-15: Comparison of emission of CO2 equivalents when MLWT = 1 ......................... 51
Figure 4-16: Comparison of emission of CO2 equivalents when MLWT = 2 .......................... 52
Figure 4-17: Comparison of emission of CO2 equivalents when MLWT = 3 .......................... 53
Figure 4-18: Overview of washing machine’s rated capacity vs. MLWT ................................ 54
Figure 4-19: CO2 equivalents emission split by individual resource consumption
share................................................................................................................ 55
FIGURES 89
Figure 4-20: Time exposure in dependence of the rated capacity, household size
and MLWT (Starting with maximal laundry waiting time of “up to 1
week” (Chart a) to maximal laundry waiting time of “up to 4 weeks”
(Chart d)). ........................................................................................................ 56
Figure 4-21: Comparison of average washing temperatures in dependence of the
household size: 1-person household (4-21a) – 4-person household (4-
21d) ................................................................................................................. 57
FIGURES 90
TABLES 91
11 List of tables
Table 3-1: List of tested washing machines .......................................................................... 19
Table 3-2: Equipment used for the normalization process of the load ................................... 20
Table 3-3: Soil strips and respective batch number used for the tests .................................. 20
Table 3-4: Detergent ............................................................................................................ 20
Table 3-5: Overview of software used .................................................................................. 21
Table 3-6: Loading scenarios for different washing machines’ rated capacities .................... 21
Table 3-7: Test design and variation of the parameters ........................................................ 22
Table 3-8: CIE Y values of different batches and extrapolated values for 110g of
detergent ......................................................................................................... 25
Table 3-9: Testing conditions in accordance with EN60456:2005 ......................................... 25
Table 3-10: Overview of CO2 conversion factors.................................................................. 26
Table 4-1: Ratio between the main wash water consumption and the total water
consumption (mean values), in dependence of the detergent dosage .............. 35
Table 4-2: Ratio between the main wash water consumption and the total water
consumption (mean values), in dependence of the load size ........................... 35
Table 4-3: Overview of average washing performance achieved at different washing
temperatures .................................................................................................... 39
Table 4-4: Overview of different average durations of the main wash at the following
washing temperatures ...................................................................................... 40
Table 4-5: Overview of average actual washing temperatures that were achieved
instead of the respective nominal temperature ................................................. 40
Table 4-6: Summary statistics, correlations, and results from the regression analysis
(water consumption) ........................................................................................ 42
TABLES 92
Table 4-7: Summary statistics, correlations and results from the regression analysis
(energy consumtion) ........................................................................................ 43
Table 4-8: Correlations between predictor variables ............................................................. 44
Table 4-9: Summary statistics, correlations and results from the regression analysis
(detergent consumption) .................................................................................. 45
Table 4-10: Collinearity statistics .......................................................................................... 45
Appendix
Table 12-1: Indesit IWB 5125) 5 kg rated capacity .................................................................. I
Table 12-2: Miele W1514WPS, 5 kg rated capacity ................................................................ II
Table 12-3: BOSCH maxx 6 Eco Wash, 6 kg rated capacity ................................................. III
Table 12-4: AEG Öko Lavamat 76850, 7 kg rated capacity .................................................. IV
Table 12-5: Bauknecht WA UNIQ 714FLD, 7kg rated capacity ............................................. VI
Table 12-6: BoschLogix8, 8kg rated capacity ...................................................................... VII
Table 12-7: Haier HWF1481, 8 kg rated capacity ............................................................... VIII
Table 12-8: INDESIT PWE 8168W, 8kg rated capacity ........................................................ IX
Table 12-9: Bauknecht WAB-1210, 11kg rated capacity……………….................………… X
APPENDIX I
12 Appendix
12.1 Washing machine tests data
Table 11-1: Indesit IWB 5125) 5 kg rated capacity
Lo
ad s
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5,00 50 0,42 0,31 63,7 15,5 48,2 29 41 30 0,81
5,00 50 0,82 0,73 40,8 16,6 24,3 39 84 40 0,91
5,00 50 0,94 0,85 39,5 16,5 23,0 21 84 60 0,94
5,00 100 0,43 0,34 64,0 16,5 47,5 18 41 30 0,87
5,00 100 0,80 0,71 40,5 16,8 23,7 16 84 40 0,98
5,00 100 0,95 0,86 40,8 17,1 23,8 16 83 60 1,00
5,00 150 0,45 0,34 64,4 16,1 48,4 17 41 30 0,90
5,00 150 0,79 0,70 40,4 16,7 23,8 16 83 40 1,02
5,00 150 0,92 0,84 38,6 17,0 21,6 16 83 60 1,04
3,75 42,5 0,40 0,30 58,7 13,6 45,1 17 40 30 0,82
3,75 42,5 0,74 0,65 36,3 14,5 21,8 16 83 40 0,93
3,75 42,5 0,94 0,85 36,9 13,8 23,1 16 82 60 0,97
3,75 85 0,39 0,30 58,2 13,5 44,7 16 40 30 0,90
3,75 85 0,73 0,64 35,8 14,3 21,5 16 82 40 1,01
3,75 85 0,91 0,83 35,7 14,0 21,6 16 82 60 1,04
3,75 127,5 0,41 0,31 58,6 13,7 44,9 16 39 30 0,94
3,75 127,5 0,68 0,60 34,9 14,1 20,9 16 82 40 1,04
3,75 127,5 0,90 0,82 33,3 14,4 18,9 19 83 60 1,08
2,50 35 0,36 0,28 54,0 11,3 42,6 17 38 30 0,85
2,50 35 0,67 0,59 30,8 12,1 18,8 16 81 40 0,96
2,50 35 0,88 0,80 30,6 11,4 19,2 16 81 60 0,98
2,50 70 0,35 0,26 53,9 11,2 42,7 16 38 30 0,92
2,50 70 0,62 0,55 29,7 11,2 18,5 16 81 40 1,02
2,50 70 0,92 0,84 30,2 11,5 18,6 15 81 60 1,07
2,50 105 0,34 0,25 52,9 10,9 42,1 16 38 30 0,96
2,50 105 0,65 0,57 30,5 11,5 18,9 16 81 40 1,07
2,50 105 0,91 0,83 30,2 11,5 18,7 15 81 60 1,13
1,25 27,5 0,30 0,21 46,3 7,7 38,6 17 37 30 0,91
1,25 27,5 0,54 0,46 23,0 8,7 14,4 15 80 40 1,01
1,25 27,5 0,79 0,72 23,3 8,3 15,0 15 81 60 1,05
APPENDIX II
1,25 55 0,31 0,22 47,3 7,7 39,7 16 37 30 0,98
1,25 55 0,56 0,48 22,8 8,1 14,7 15 81 40 1,08
1,25 55 0,76 0,68 22,3 8,4 13,9 16 81 60 1,13
1,25 82,5 0,30 0,22 45,0 7,5 37,5 16 36 30 0,92
1,25 82,5 0,53 0,46 23,9 8,8 15,1 21 81 40 1,12
1,25 82,5 0,75 0,68 21,6 8,0 13,6 19 81 60 1,17
0,00 0 0,23 0,16 38,6 5,3 33,4 16 35 30
0,00 0 0,38 0,32 16,7 5,7 11,0 25 80 40
0,00 0 0,54 0,48 16,3 5,8 10,4 15 81 60
Table 11-2: Miele W1514WPS, 5 kg rated capacity
Load
siz
e in
kg
Det
ergen
t
dosa
ge
in g
En
erg
y
con
sum
pti
on
in
kW
h
En
erg
y
con
sum
pti
on
in
main
wash
in
kW
h
Wa
ter
con
sum
pti
on
in L
Wa
ter
con
sum
pti
on
main
wash
in
L
Wa
ter
con
sum
pti
on
rin
se c
ycl
e i
n L
Du
rati
on
spin
nin
g p
ha
se
in m
in
Du
rati
on
main
wash
in
min
Wash
ing
tem
per
atu
re i
n
°C
Wash
ing
Per
form
an
ce
Ind
ex
5,00 50 0,29 0,20 42,8 13,1 29,7 8 52 30 0,93
5,00 50 0,31 0,21 53,0 13,1 39,9 10 71 30 0,88
5,00 50 0,46 0,36 51,9 12,7 39,2 9 71 40 0,95
5,00 50 0,79 0,69 40,8 12,3 28,5 9 63 60 0,98
5,00 100 0,36 0,25 47,8 13,1 34,7 9 71 30 0,99
5,00 100 0,32 0,22 54,6 14,4 40,2 9 71 30 1,00
5,00 100 0,44 0,36 44,2 13,4 30,8 8 52 40 1,02
5,00 100 0,45 0,35 53,0 13,3 39,7 9 71 40 1,00
5,00 100 0,79 0,70 40,8 12,8 28,0 9 63 60 1,06
5,00 150 0,27 0,19 39,8 13,2 26,6 8 52 30 1,01
5,00 150 0,31 0,21 54,3 14,2 40,1 10 71 30 0,97
5,00 150 0,50 0,39 49,8 12,9 36,9 9 71 40 1,06
5,00 150 0,79 0,71 40,5 13,0 27,5 9 63 60 1,13
3,75 42,5 0,22 0,14 32,5 9,7 22,8 8 52 30 0,89
3,75 42,5 0,34 0,27 35,1 11,0 24,1 8 52 40 0,93
3,75 42,5 0,65 0,57 39,6 10,8 28,8 8 52 60 0,97
3,75 85 0,21 0,13 39,5 11,0 28,5 8 52 30 0,95
3,75 85 0,37 0,27 39,6 10,7 28,9 8 52 40 1,00
3,75 85 0,66 0,59 40,4 11,0 29,4 8 52 60 1,05
3,75 127,5 0,23 0,15 39,8 11,5 28,3 8 52 30 1,00
3,75 127,5 0,35 0,27 39,9 11,0 28,9 8 52 40 1,02
3,75 127,5 0,67 0,60 39,4 10,9 28,5 8 52 60 1,12
2,50 35 0,21 0,14 31,7 9,3 22,4 8 52 30 0,94
2,50 35 0,38 0,30 34,4 10,6 23,8 8 52 40 0,98
2,50 35 0,70 0,62 36,7 10,3 26,4 8 52 60 1,03
APPENDIX III
2,50 70 0,24 0,16 34,1 10,6 23,5 8 52 30 1,00
2,50 70 0,38 0,31 33,9 10,6 23,3 8 52 40 1,05
2,50 70 0,72 0,64 37,5 11,0 26,5 8 52 60 1,12
2,50 105 0,23 0,15 32,5 9,7 22,8 8 52 30 1,04
2,50 105 0,35 0,27 32,9 10,2 22,7 8 52 40 1,08
2,50 105 0,69 0,62 35,8 10,1 25,7 8 52 60 1,17
1,25 27,5 0,17 0,11 20,2 6,7 13,5 5 52 30 0,98
1,25 27,5 0,25 0,19 19,8 6,5 13,3 5 52 40 1,02
1,25 27,5 0,49 0,43 20,2 6,4 13,8 5 52 60 1,06
1,25 55 0,17 0,10 20,0 6,8 13,2 6 52 30 1,05
1,25 55 0,26 0,20 19,7 6,5 13,2 5 52 40 1,01
1,25 55 0,49 0,43 19,7 6,5 13,2 5 52 60 1,14
1,25 82,5 0,17 0,10 25,2 6,4 18,8 6 52 30 1,08
1,25 82,5 0,14 0,12 22,2 7,6 14,6 6 52 30 1,08
1,25 82,5 0,26 0,20 19,4 8,4 11,0 6 52 40 1,13
1,25 82,5 0,47 0,41 18,6 6,2 12,4 6 52 60 1,19
0,00 0 0,16 0,11 21,4 7,3 14,1 6 52 30
0,00 0 0,25 0,20 21,2 7,3 13,9 6 52 40
0,00 0 0,46 0,42 21,4 7,5 13,9 6 52 60
Table 11-3: BOSCH maxx 6 Eco Wash, 6 kg rated capacity
Load
siz
e in
kg
Det
ergen
t d
osa
ge
in g
En
ergy
con
sum
pti
on
in
kW
h
En
ergy
con
sum
pti
on
in
main
wash
in
kW
h
Wate
r
con
sum
pti
on
in L
Wate
r
con
sum
pti
on
main
wash
in
L
Wate
r
con
sum
pti
on
rin
se
cycl
e i
n L
Du
rati
on
sp
inn
ing
ph
ase
in
min
Du
rati
on
main
wash
in
min
Wash
ing
tem
per
atu
re i
n °
C
Wash
ing
Per
form
an
ce
Ind
ex
6,00 56 0,26 0,16 53,1 16,4 36,7 15 19 30 0,71
6,00 56 0,39 0,29 56,4 15,8 40,6 13 23 40 0,74
6,00 56 0,91 0,82 52,1 15,6 36,5 13 41 60 0,82
6,00 112 0,23 0,14 52,5 16,8 35,7 13 18 30 0,76
6,00 112 0,42 0,32 55,2 15,9 39,3 13 24 40 0,81
6,00 112 0,90 0,81 51,6 15,3 36,3 15 41 60 0,90
6,00 168 0,21 0,12 50,9 14,9 36,0 13 18 30 0,75
6,00 168 0,41 0,32 50,7 16,1 34,6 13 24 40 0,83
6,00 168 0,88 0,79 54,1 15,7 38,4 13 41 60 0,96
4,50 47 0,27 0,18 49,3 14,7 34,6 15 19 30 0,79
4,50 47 0,53 0,44 50,6 14,9 35,7 13 28 40 0,84
4,50 47 0,92 0,83 48,2 13,6 34,6 13 42 60 0,90
4,50 94 0,24 0,15 49,5 15,1 34,4 12 17 30 0,83
4,50 94 0,53 0,44 51,7 15,2 36,5 13 28 40 0,92
APPENDIX IV
4,50 94 0,90 0,82 47,8 13,5 34,3 13 42 60 0,98
4,50 141 0,24 0,15 49,2 14,9 34,3 13 19 30 0,87
4,50 141 0,51 0,42 49,5 15,2 34,3 13 28 40 0,94
4,50 141 0,94 0,85 49,0 14,0 35,0 13 43 60 1,04
3,00 38 0,27 0,18 45,8 11,7 34,1 13 19 30 0,79
3,00 38 0,46 0,37 46,6 12,2 34,4 12 26 40 0,86
3,00 38 0,78 0,69 45,4 10,8 34,6 13 37 60 0,93
3,00 76 0,29 0,19 45,9 11,9 34,0 16 20 30 0,87
3,00 76 0,44 0,35 46,3 11,8 34,5 13 25 40 0,92
3,00 76 0,81 0,73 45,8 11,2 34,6 13 37 60 1,01
3,00 114 0,24 0,15 46,4 12,2 34,2 13 18 30 0,91
3,00 114 0,47 0,39 46,4 12,0 34,4 13 27 40 0,96
3,00 114 0,75 0,67 45,4 10,7 34,7 12 36 60 1,07
1,50 29 0,24 0,14 43,0 8,6 34,4 14 18 30 0,82
1,50 29 0,40 0,30 43,0 8,7 34,3 12 24 40 0,93
1,50 29 0,66 0,57 42,7 8,3 34,4 14 33 60 0,97
1,50 58 0,24 0,14 43,5 9,1 34,4 16 18 30 0,91
1,50 58 0,39 0,30 43,6 9,0 34,6 14 24 40 0,97
1,50 58 0,64 0,55 42,7 8,2 34,5 12 33 60 1,04
1,50 87 0,24 0,14 43,4 8,9 34,5 16 17 30 0,93
1,50 87 0,38 0,30 30,0 9,1 20,9 15 24 40 0,99
1,50 87 0,42 0,32 42,4 8,9 33,5 14 24 40 1,09
1,50 87 0,63 0,54 42,6 8,1 34,5 13 32 60 1,00
0,00 0 0,18 0,11 22,9 5,6 17,3 12 17 30
0,00 0 0,27 0,20 22,8 5,5 17,3 12 21 40
0,00 0 0,43 0,36 22,0 4,7 17,3 12 27 60
Table 11-4: AEG Öko Lavamat 76850, 7 kg rated capacity
Lo
ad
siz
e in
kg
Det
ergen
t
do
sag
e in
g
En
erg
y
con
sum
pti
on
in
kW
h
En
erg
y
con
sum
pti
on
in
ma
in w
ash
in
kW
h
Wa
ter
con
sum
pti
on
in L
Wa
ter
con
sum
pti
on
ma
in w
ash
in
L
Wa
ter
con
sum
pti
on
rin
se c
ycl
e i
n L
Du
rati
on
spin
nin
g p
ha
se
in m
in
Du
rati
on
main
wa
sh in
min
Wa
shin
g
tem
per
atu
re i
n
°C
Wa
shin
g
Per
form
an
ce
Ind
ex
7,00 62 0,42 0,28 59,8 18,2 41,6 17 63 30 0,82
7,00 62 0,63 0,50 62,1 19,4 42,7 14 67 40 0,88
7,00 62 1,26 1,12 62,9 19,6 43,3 14 89 60 0,90
7,00 124 0,42 0,26 59,2 18,0 41,2 23 62 30 0,86
7,00 124 0,73 0,61 61,1 19,4 41,7 17 73 40 0,96
7,00 124 1,16 1,03 61,7 18,2 43,5 19 87 60 1,03
APPENDIX V
7,00 186 0,44 0,31 60,0 18,2 41,8 13 65 30 0,92
7,00 186 0,66 0,53 60,7 18,1 42,6 17 70 40 1,00
7,00 186 1,20 1,07 61,2 18,1 43,1 14 88 60 1,06
5,25 51,5 0,44 0,32 60,4 18,1 42,3 14 66 30 0,89
5,25 51,5 0,80 0,66 60,7 18,2 42,5 16 75 40 0,93
5,25 51,5 1,24 1,12 62,1 18,1 44,0 15 90 60 0,96
5,25 103 0,50 0,36 62,6 18,7 43,9 17 67 30 0,96
5,25 103 0,73 0,58 61,7 17,9 43,8 16 74 40 1,01
5,25 103 1,23 1,11 62,1 18,2 43,9 18 91 60 1,06
5,25 154,5 0,46 0,33 61,5 18,0 43,5 14 65 30 1,01
5,25 154,5 0,74 0,62 61,9 18,0 43,9 18 75 40 1,04
5,25 154,5 1,22 1,09 62,0 18,1 43,9 14 89 60 1,11
3,50 41 0,42 0,29 55,2 14,5 40,7 18 67 30 0,91
3,50 41 0,60 0,47 46,5 11,7 34,8 15 68 40 0,95
3,50 41 0,69 0,57 55,8 14,5 41,3 14 75 40 0,97
3,50 41 0,86 0,74 44,3 11,5 32,8 14 75 60 0,97
3,50 41 1,04 0,91 53,0 13,6 39,4 17 81 60 1,02
3,50 82 0,42 0,29 56,7 14,6 42,1 17 64 30 0,97
3,50 82 0,70 0,57 54,9 14,7 40,2 16 76 40 1,03
3,50 82 0,92 0,79 47,0 11,6 35,4 21 77 60 1,00
3,50 82 1,13 1,00 54,4 14,6 39,8 17 87 60 1,01
3,50 123 0,48 0,31 56,4 14,5 41,9 30 66 30 1,02
3,50 123 0,72 0,60 56,3 14,6 41,7 14 76 40 1,07
3,50 123 0,91 0,79 46,2 11,8 34,4 14 75 60 1,11
3,50 123 1,07 0,93 53,8 13,9 39,9 16 82 60 1,14
1,75 30,5 0,41 0,29 40,6 11,7 28,9 17 64 30 0,95
1,75 30,5 0,62 0,50 41,4 11,9 29,5 15 71 40 0,98
1,75 30,5 0,98 0,86 41,4 12,0 29,4 15 79 60 1,01
1,75 61 0,37 0,24 40,7 11,8 28,9 15 62 30 1,01
1,75 61 0,61 0,48 41,3 11,8 29,5 16 70 40 1,05
1,75 61 0,97 0,85 41,9 12,0 29,9 14 78 60 1,11
1,75 91,5 0,38 0,26 40,1 11,7 28,4 14 63 30 1,05
1,75 91,5 0,60 0,48 41,2 11,7 29,5 14 70 40 1,10
1,75 91,5 0,99 0,87 41,8 12,0 29,8 14 79 60 1,16
0,00 0 0,38 0,27 33,5 12,2 21,3 14 65 30
0,00 0 0,58 0,48 32,8 12,1 20,7 14 71 40
0,00 0 0,95 0,85 32,6 12,2 20,4 14 79 60
APPENDIX VI
Table 11-5: Bauknecht WA UNIQ 714FLD, 7kg rated capacity
Lo
ad
siz
e in
kg
Det
ergen
t d
osa
ge
in g
En
erg
y
con
sum
pti
on
in
kW
h
En
erg
y
con
sum
pti
on
in
ma
in w
ash
in
kW
h
Wa
ter
con
sum
pti
on
in L
Wa
ter
con
sum
pti
on
ma
in w
ash
in
L
Wa
ter
con
sum
pti
on
rin
se c
ycl
e i
n L
Du
rati
on
spin
nin
g p
ha
se i
n
min
Du
rati
on
main
wa
sh
in m
in
Wa
shin
g
tem
per
atu
re i
n
°C
Wa
shin
g
Per
form
an
ce
Ind
ex
7,00 62 0,44 0,28 101,1 19,3 81,8 21 45 30 0,84
7,00 62 0,63 0,46 105,2 20,1 85,0 20 44 40 0,84
7,00 62 0,98 0,87 53,3 17,5 35,8 22 87 60 0,99
7,00 124 0,41 0,25 99,5 19,1 80,4 23 45 30 0,85
7,00 124 0,53 0,36 96,9 18,8 78,1 18 45 40 0,90
7,00 124 0,97 0,86 56,6 17,8 38,8 19 87 60 1,04
7,00 186 0,45 0,28 104,0 19,9 84,1 23 45 30 0,89
7,00 186 0,59 0,42 104,1 19,9 84,2 19 44 40 0,92
7,00 186 1,01 0,90 54,5 17,6 36,9 17 88 60 1,12
5,25 51,5 0,39 0,26 68,4 17,3 51,2 19 76 30 0,84
5,25 51,5 0,62 0,49 67,4 16,2 51,2 24 77 40 0,91
5,25 51,5 1,04 0,93 53,0 16,2 36,8 17 87 60 0,96
5,25 103 0,37 0,24 65,4 16,5 49,0 24 75 30 0,92
5,25 103 0,61 0,49 65,9 15,8 50,1 26 77 40 0,98
5,25 103 1,04 0,93 54,4 16,2 38,2 16 87 60 1,04
5,25 154,5 0,41 0,28 66,8 16,6 50,2 21 76 30 0,98
5,25 154,5 0,65 0,52 66,8 16,5 50,3 32 78 40 1,04
5,25 154,5 1,04 0,93 52,9 15,2 37,7 26 86 60 1,11
3,50 41 0,47 0,34 57,9 13,8 44,1 20 75 30 0,91
3,50 41 0,64 0,52 57,7 14,0 43,6 18 77 40 0,96
3,50 41 1,02 0,90 43,1 13,7 29,3 18 85 60 0,99
3,50 82 0,46 0,34 57,9 13,8 44,1 22 76 30 0,99
3,50 82 0,65 0,53 56,9 13,7 43,2 19 77 40 1,01
3,50 82 1,04 0,91 42,9 13,7 29,3 23 84 60 1,08
3,50 123 0,45 0,32 57,1 13,8 43,3 18 75 30 1,02
3,50 123 0,65 0,52 56,4 13,7 42,7 20 77 40 1,06
3,50 123 1,05 0,94 45,4 13,8 31,6 24 84 60 1,14
1,75 30,5 0,51 0,40 56,2 13,6 42,6 26 75 30 0,97
1,75 30,5 0,71 0,59 56,3 13,4 42,9 26 76 40 1,02
1,75 30,5 1,07 0,97 43,0 13,7 29,4 18 83 60 1,01
1,75 61 0,50 0,39 56,6 13,6 43,0 18 74 30 1,05
1,75 61 0,72 0,60 57,1 13,7 43,4 21 76 40 1,06
1,75 61 1,08 0,97 42,5 13,8 28,7 19 83 60 1,12
1,75 91,5 0,50 0,38 56,5 13,7 42,8 24 75 30 1,08
APPENDIX VII
1,75 91,5 0,72 0,60 56,7 13,5 43,2 19 76 40 1,12
1,75 91,5 1,06 0,96 42,4 13,5 28,9 16 83 60 1,17
0,00 0 0,20 0,14 23,2 6,6 16,6 9 28 30
0,00 0 0,29 0,24 22,9 6,6 16,3 9 28 40
0,00 0 0,47 0,42 23,0 6,6 16,4 9 28 60
Table 11-6: BoschLogix8, 8kg rated capacity
Lo
ad
siz
e in
kg
Det
ergen
t
do
sag
e in
g
En
erg
y c
on
sum
pti
on
in
kW
h
En
erg
y c
on
sum
pti
on
in m
ain
wa
sh i
n k
Wh
Wa
ter
con
sum
pti
on
in L
Wa
ter
con
sum
pti
on
ma
in w
ash
in
L
Wa
ter
con
sum
pti
on
rin
se c
ycl
e i
n L
Du
rati
on
sp
inn
ing
ph
ase
in
min
Du
rati
on
main
wa
sh
in m
in
Wa
shin
g
tem
per
atu
re i
n °
C
Wa
shin
g
Per
form
an
ce I
nd
ex
8,00 68 0,26 0,13 78,5 19,8 58,7 11 87 30 0,79
8,00 68 0,76 0,66 79,4 20,8 58,6 11 100 40 0,87
8,00 68 1,00 0,89 78,4 19,8 58,6 12 107 60 0,88
8,00 136 0,30 0,20 78,4 19,8 58,6 12 87 30 0,86
8,00 136 0,78 0,68 79,6 20,9 58,7 12 100 40 0,96
8,00 136 0,99 0,89 78,4 19,8 58,6 12 107 60 0,99
8,00 204 0,29 0,18 78,6 19,8 58,8 11 87 30 0,90
8,00 204 0,77 0,67 79,6 20,9 58,7 11 100 40 0,97
8,00 204 1,15 1,06 78,6 19,9 58,7 12 107 60 1,06
6,00 56 0,35 0,25 78,5 19,9 58,6 12 86 30 0,89
6,00 56 0,82 0,72 79,4 20,9 58,5 11 100 40 0,95
6,00 56 1,24 1,12 78,4 19,8 58,6 11 107 60 0,97
6,00 112 0,32 0,22 78,4 19,8 58,6 11 87 30 0,95
6,00 112 0,81 0,71 79,5 20,9 58,6 12 100 40 1,01
6,00 112 1,22 1,10 78,4 19,8 58,6 16 107 60 1,06
6,00 168 0,32 0,21 78,4 19,8 58,6 12 87 30 0,98
6,00 168 0,81 0,71 79,4 20,9 58,5 12 100 40 1,06
6,00 168 1,23 1,13 78,4 19,8 58,6 11 107 60 1,11
4,00 44 0,26 0,15 58,6 14,1 44,5 12 71 30 0,89
4,00 44 0,62 0,53 58,6 14,1 44,5 11 83 40 0,96
4,00 44 0,89 0,80 58,6 14,1 44,5 12 92 60 1,00
4,00 88 0,22 0,13 58,6 14,1 44,5 11 72 30 0,97
4,00 88 0,63 0,54 58,6 14,1 44,5 11 83 40 1,03
4,00 88 0,92 0,82 58,6 14,1 44,5 13 92 60 1,07
4,00 132 0,24 0,14 58,6 14,1 44,5 12 72 30 0,99
4,00 132 0,60 0,50 58,6 14,1 44,5 13 83 40 1,07
4,00 132 0,92 0,83 58,6 14,1 44,5 14 92 60 1,14
2,00 32 0,29 0,20 49,2 11,5 37,7 12 62 30 0,95
APPENDIX VIII
2,00 32 0,51 0,42 49,2 11,5 37,7 11 73 40 1,00
2,00 32 0,81 0,72 49,2 11,5 37,7 12 82 60 1,04
2,00 64 0,27 0,17 49,1 11,5 37,6 13 62 30 1,00
2,00 64 0,51 0,42 49,2 11,5 37,7 12 72 40 1,06
2,00 64 0,84 0,74 49,2 11,5 37,7 12 82 60 1,11
2,00 96 0,27 0,18 49,2 11,5 37,7 11 62 30 1,03
2,00 96 0,58 0,48 49,2 11,5 37,7 15 72 40 1,10
2,00 96 0,83 0,73 49,2 11,5 37,7 13 82 60 1,15
0,00 0 0,17 0,11 22,9 6,3 16,6 11 42 30
0,00 0 0,34 0,28 22,9 6,4 16,5 11 53 40
0,00 0 0,47 0,41 22,9 6,3 16,6 11 62 60
Table 11-7: Haier HWF1481, 8 kg rated capacity
Load
siz
e in
kg
Det
ergen
t d
osa
ge i
n
g
En
ergy c
on
sum
pti
on
in k
Wh
En
ergy c
on
sum
pti
on
in m
ain
wash
in
kW
h
Wate
r co
nsu
mp
tio
n
in L
Wate
r co
nsu
mp
tio
n
main
wash
in
L
Wate
r co
nsu
mp
tio
n
rin
se c
ycl
e i
n L
Du
rati
on
sp
inn
ing
ph
ase
in
min
Du
rati
on
main
wash
in m
in
Wash
ing
tem
per
atu
re i
n °
C
Wash
ing
Per
form
an
ce I
nd
ex
8,00 68 0,26 0,16 63,2 21,1 42,1 15 61 30 0,77
8,00 68 0,41 0,33 65,5 22,0 43,5 21 61 40 0,82
8,00 68 1,25 1,16 64,2 20,8 43,4 25 73 60 0,90
8,00 136 0,22 0,16 63,5 21,1 42,4 16 61 30 0,88
8,00 136 0,44 0,36 63,0 21,2 41,8 23 61 40 0,91
8,00 136 1,26 1,20 59,9 20,5 60 1,00
8,00 136 1,32 1,25 64,1 21,4 60 1,03
8,00 136 1,26 1,15 59,9 21,0 60 1,00
8,00 204 0,21 0,14 65,4 22,4 43,1 17 61 30 0,89
8,00 204 0,48 0,40 61,2 20,9 40,3 16 61 40 0,96
8,00 204 1,18 1,10 64,3 21,5 42,8 18 72 60 1,04
6,00 56 0,26 0,18 59,1 18,6 40,4 15 61 30 0,83
6,00 56 0,56 0,49 60,1 18,9 41,2 14 61 40 0,88
6,00 56 1,15 1,08 57,3 17,5 39,8 15 72 60 0,94
6,00 112 0,28 0,19 60,3 18,9 41,4 18 61 30 0,91
6,00 112 0,60 0,52 58,7 19,2 39,5 15 61 40 0,95
6,00 112 1,15 1,07 61,2 17,5 43,7 21 72 60 1,01
6,00 168 0,29 0,21 59,3 19,6 39,7 16 61 30 0,94
6,00 168 0,62 0,55 61,4 19,8 41,5 15 61 40 1,00
6,00 168 1,15 1,08 59,1 18,0 41,1 24 72 60 1,09
4,00 44 0,27 0,19 51,9 14,1 37,8 16 61 30 0,87
4,00 44 0,45 0,38 52,0 14,1 37,9 14 61 40 0,91
APPENDIX IX
4,00 44 1,08 1,00 53,2 15,1 38,1 17 72 60 0,98
4,00 88 0,29 0,20 54,1 15,9 38,2 14 61 30 0,95
4,00 88 0,50 0,42 53,4 15,4 38,0 15 61 40 0,99
4,00 88 1,06 0,98 54,1 15,0 39,1 15 72 60 1,06
4,00 132 0,24 0,17 51,9 15,1 36,9 14 61 30 0,99
4,00 132 0,44 0,37 52,2 15,5 36,8 15 61 40 1,01
4,00 132 0,98 0,91 54,7 16,0 38,6 17 72 60 1,11
2,00 32 0,25 0,17 38,4 10,5 27,9 26 61 30 0,92
2,00 32 0,41 0,34 38,4 10,6 27,8 19 61 40 0,96
2,00 32 0,84 0,77 38,2 10,8 27,4 14 73 60 1,02
2,00 64 0,24 0,16 37,7 10,1 27,6 24 61 30 0,98
2,00 64 0,41 0,33 38,2 10,3 27,9 14 61 40 1,01
2,00 64 0,80 0,72 38,1 10,4 27,8 14 72 60 1,09
2,00 96 0,25 0,17 38,0 10,6 27,4 20 62 30 1,06
2,00 96 0,39 0,32 37,1 10,2 27,0 13 61 40 1,12
2,00 96 0,82 0,75 38,2 10,6 27,6 14 72 60 1,18
0,00 0 0,20 0,14 38,6 7,5 31,1 26 61 30
0,00 0 0,32 0,26 38,3 7,5 30,9 16 61 40
0,00 0 0,60 0,54 38,6 7,6 31,0 21 72 60
Table 11-8: INDESIT PWE 8168W, 8kg rated capacity
Load
siz
e in
kg
Det
ergen
t d
osa
ge i
n
g
En
ergy
con
sum
pti
on
in
kW
h
En
ergy
con
sum
pti
on
in
main
wash
in
kW
h
Wate
r
con
sum
pti
on
in
L
Wate
r
con
sum
pti
on
main
wash
in
L
Wate
r
con
sum
pti
on
rin
se
cycl
e i
n L
Du
rati
on
sp
inn
ing
ph
ase
in
min
Du
rati
on
main
wash
in
min
Wash
ing
tem
per
atu
re i
n °
C
Wash
ing
Per
form
an
ce I
nd
ex
8,00 68 0,47 0,35 70,6 23,7 46,9 20 34 30 0,75
8,00 68 1,15 1,03 73,5 25,9 47,6 19 161 40 0,93
8,00 68 1,33 1,21 72,1 25,3 46,8 22 161 60 0,96
8,00 136 0,47 0,34 73,2 24,2 49,0 22 42 30 0,82
8,00 136 1,10 0,98 74,2 25,5 48,7 19 161 40 1,02
8,00 136 1,34 1,23 74,2 27,4 46,8 19 161 60 1,04
8,00 204 0,43 0,32 70,7 24,1 46,6 18 41 30 0,87
8,00 204 1,10 1,00 72,5 26,0 46,5 21 161 40 1,08
8,00 204 1,33 1,21 71,1 24,8 46,3 33 161 60 1,09
6,00 56 0,38 0,29 63,4 20,2 43,2 19 31 30 0,76
6,00 56 1,10 0,97 67,3 23,0 44,3 20 162 40 0,97
6,00 56 1,33 1,23 64,4 21,4 43,0 20 161 60 0,99
6,00 112 0,43 0,32 63,1 21,0 42,1 19 41 30 0,87
6,00 112 1,03 0,93 65,9 22,3 43,5 22 161 40 1,06
6,00 112 1,34 1,24 66,4 22,2 44,3 19 161 60 1,09
APPENDIX X
6,00 168 0,42 0,31 63,6 20,9 42,6 21 41 30 0,91
6,00 168 1,04 0,93 65,6 22,2 43,4 19 161 40 1,10
6,00 168 1,34 1,24 66,6 22,5 44,1 19 161 60 1,14
4,00 44 0,36 0,25 54,2 15,4 38,8 19 26 30 0,79
4,00 44 0,88 0,78 56,6 17,3 39,3 21 160 40 0,97
4,00 44 1,22 1,11 57,6 17,9 39,7 19 155 60 1,01
4,00 88 0,33 0,23 53,9 15,6 38,3 19 26 30 0,85
4,00 88 0,96 0,85 56,5 18,0 38,6 19 160 40 1,05
4,00 88 1,22 1,12 57,0 17,9 39,1 19 156 60 1,10
4,00 132 0,38 0,26 54,8 16,3 38,5 22 26 30 1,09
4,00 132 0,95 0,86 58,2 18,1 40,1 18 161 40 1,14
4,00 132 1,20 1,11 56,6 17,8 38,8 19 156 60 0,88
2,00 32 0,29 0,20 42,2 11,2 31,0 20 22 30 0,81
2,00 32 0,74 0,64 43,1 12,1 31,0 25 159 40 1,04
2,00 32 0,93 0,84 42,8 12,8 30,1 32 152 60 1,07
2,00 64 0,28 0,19 41,2 11,5 29,7 19 23 30 0,90
2,00 64 0,76 0,67 41,8 12,4 29,4 19 159 40 1,10
2,00 64 0,94 0,84 41,2 12,2 29,0 27 153 60 1,15
2,00 96 0,30 0,21 41,3 11,2 30,1 19 23 30 0,95
2,00 96 0,70 0,60 41,4 11,7 29,8 19 159 40 1,15
2,00 96 0,93 0,84 42,9 12,4 30,4 20 147 60 1,19
0,00 0 0,19 0,11 30,9 6,2 24,7 22 21 30
0,00 0 0,45 0,38 32,1 7,0 25,1 18 158 40
0,00 0 0,57 0,49 31,6 6,8 24,8 18 147 60
Table 11-9: Bauknecht WAB-1210, 11kg rated capacity
Lo
ad
siz
e in
kg
Det
ergen
t d
osa
ge i
n
g
En
ergy
con
sum
pti
on
in
kW
h
En
ergy
con
sum
pti
on
in
ma
in w
ash
in
kW
h
Wa
ter
con
sum
pti
on
in L
Wa
ter
con
sum
pti
on
ma
in w
ash
in
L
Wa
ter
con
sum
pti
on
rin
se c
ycl
e i
n L
Du
rati
on
sp
inn
ing
ph
ase
in
min
Du
rati
on
main
wash
in m
in
Wa
shin
g
tem
per
atu
re i
n °
C
Wa
shin
g
Per
form
an
ce I
nd
ex
11,00 86 0,74 0,59 82,8 25,5 56,7 9 169 30 0,90
11,00 172 0,77 0,56 82,4 25,5 56,3 9 169 30 1,02
11,00 258 0,71 0,56 82,7 25,5 56,3 9 169 30 1,04
8,25 69,5 1,00 0,78 84,0 26,5 57,3 9 167 30 0,97
8,25 139 0,97 0,78 83,2 25,6 54,8 8 167 30 1,04
8,25 208,5 0,94 0,78 83,2 25,5 56,8 8 167 30 1,07
5,50 53 0,67 0,55 55,0 16,8 37,4 8 173 30 0,97
5,50 106 0,63 0,50 55,0 17,0 37,5 8 173 30 1,04
APPENDIX XI
5,50 159 0,68 0,54 55,0 16,4 36,9 8 173 30 1,08
2,75 36,5 0,50 0,40 42,1 12,3 28,3 8 124 30 0,96
2,75 73 0,56 0,46 45,8 13,6 30,9 8 124 30 1,07
2,75 109,5 0,51 0,41 42,7 12,7 28,8 8 124 30 1,13
11,00 86 0,99 0,84 82,9 25,5 56,2 9 173 40 0,96
11,00 172 1,04 0,85 82,4 25,5 56,3 9 173 40 1,03
11,00 258 1,04 0,85 83,3 26,0 56,9 9 173 40 1,08
8,25 69,5 1,35 1,16 83,4 26,1 57,3 8 175 40 0,99
8,25 139 1,31 1,15 82,7 25,7 57,0 8 174 40 1,09
8,25 208,5 1,32 1,16 82,7 25,5 57,2 8 174 40 1,11
5,50 53 0,81 0,68 53,8 16,2 36,4 8 173 40 0,99
5,50 106 0,82 0,69 55,0 16,4 37,0 8 173 40 1,08
5,50 159 0,81 0,69 54,7 16,4 37,2 8 173 40 1,11
2,75 36,5 0,66 0,56 44,6 13,1 44,6 8 124 40 0,97
2,75 73 0,68 0,58 45,4 13,5 30,6 8 124 40 1,08
2,75 109,5 0,66 0,55 44,5 13,0 29,8 8 124 40 1,14
11,00 86 1,44 1,25 82,8 25,5 57,3 8 186 60 0,95
11,00 172 1,33 1,17 82,9 25,5 57,1 9 187 60 1,05
11,00 172 1,38 1,20 82,7 25,5 57,1 9 188 60 1,05
11,00 172 1,38 1,21 82,6 25,5 57,1 9 188 60 1,03
11,00 258 1,35 1,19 82,7 25,4 57,2 9 186 60 1,09
8,25 69,5 1,78 1,53 84,0 26,8 57,9 9 190 60 1,00
8,25 139 1,66 1,50 83,6 26,1 57,5 8 189 60 1,07
8,25 208,5 1,68 1,50 83,3 25,5 57,9 8 189 60 1,14
5,50 86 1,15 1,01 55,7 17,4 38,0 60 0,99
5,50 106 1,12 0,97 54,7 16,4 37,0 8 181 60 1,07
5,50 159 1,04 0,91 53,5 15,3 35,6 8 181 60 1,14
2,75 36,5 1,02 0,91 45,2 13,3 30,6 8 125 60 1,01
2,75 73 1,01 0,92 45,8 13,6 30,9 8 125 60 1,12
2,75 109,5 1,03 0,92 47,4 13,9 31,4 8 125 60 1,18
0,00 1,12 0,97 54,0 15,4 36,4 8 181 60 0,00
12.2 Virtual washing machine MATLAB source code
function [ DET, CWmw, CEmw, vektorWASCHKORB] =
Waschmaschine(BETA, WP, TEMP, WMV, MWD, WASCHKORB, m,
WochenCounterGENERAL, RESTLOAD, REG1ODERNOT2, PERSON,
LOADamoountTOTAL,WOCHENLA, n, SZX)
if TEMP ==30;
WP = .93;
end
if TEMP ==40;
APPENDIX XII
WP = 1;
end
if TEMP ==60;
WP = 1.04;
end
if WMV ==5;
if TEMP ==30;
MWD = 48;
end
if TEMP ==40;
MWD = 69;
end
if TEMP ==60;
MWD = 68;
end
end
if WMV ==6;
if TEMP ==30;
MWD = 50;
end
if TEMP ==40;
MWD = 69;
end
if TEMP ==60;
MWD = 68;
end
end
if WMV ==7;
if TEMP ==30;
MWD = 65;
end
if TEMP ==40;
MWD = 69;
end
if TEMP ==60;
MWD = 82;
end
end
if WMV ==8;
if TEMP ==30;
MWD = 68;
end
if TEMP ==40;
MWD = 102; % Dauer des hauptwaschganges
end
if TEMP ==60;
MWD = 108; % Dauer des hauptwaschganges in minuten in einer
kg waschmaschine
APPENDIX XIII
end
end
if WMV ==9;
if TEMP ==30;
MWD = 120;
end
if TEMP ==40;
MWD = 130;
end
if TEMP ==60;
MWD = 140;
end
end
if WMV ==10;
if TEMP ==30;
MWD = 140;
end
if TEMP ==40;
MWD = 158;
end
if TEMP ==60;
MWD = 173;
end
end
if WMV ==11;
if TEMP ==30;
MWD = 156;
end
if TEMP ==40;
MWD = 158;
end
if TEMP ==60;
MWD = 173;
end
end
DET=0;
CWmw =0;
CEmw =0;
DET = ((WP - BETA.const.DET)/BETA.det.DET) -
((BETA.temp.DET*TEMP)/BETA.det.DET) -
((BETA.load.DET*WASCHKORB)/BETA.det.DET) -
((BETA.mwd.DET*MWD)/BETA.det.DET);
if DET<40
DET = 40;
end
CWmw = BETA.const.WATER + (BETA.load.WATER *WASCHKORB)+
(BETA.wmv.WATER *WMV);
APPENDIX XIV
CEmw = BETA.const.ENERGY + (BETA.temp.ENERGY * TEMP) +
(BETA.water.ENERGY * CWmw) + (BETA.mwd.ENERGY * MWD);
if REG1ODERNOT2 == 2;
RESTLOAD =0;
end
vektorWASCHKORB (1,:) = [n,m,
WochenCounterGENERAL,PERSON,LOADamoountTOTAL,WOCHENLA,
WASCHKORB, TEMP,WMV,MWD, RESTLOAD,WP, DET, CWmw,CEmw,
REG1ODERNOT2, SZX];
end
12.3 Virtual washing household MATLAB source code
CO2TOTAL=0;
PERSON =0;
myArray = zeros(7,12);
WMV=5;
MAXIMALEWARTEZEITWASCHEN = 0;
SZX=0;
for WMV=5:11;
for PERSON = 1:7;
WochenLA = 4;
Amountof30 = .23;
Amountof40 = .46;
Amountof60 = .31;
LB30 = .5;
LB40 = .7;
LB60 = .9;
MWD30 = 52;
MWD40 = 77;
MWD60 = 84;
BETA.const.DET = 0.8204235;
BETA.temp.DET = 0.002605017;
BETA.load.DET =-0.034011332;
BETA.wmv.DET =-0.000505483;
BETA.mwd.DET =0.001346586;
BETA.det.DET=0.001163081;
BETA.const.WATER =3.949488643;
BETA.load.WATER =1.703739258;
BETA.wmv.WATER =.513236840;
BETA.const.ENERGY =-.85617463;
BETA.temp.ENERGY =.02019412;
BETA.water.ENERGY =.02422291;
BETA.mwd.ENERGY =.00250646;
WP = 1.03;
Weekcounter = 0;
DOS = 52;
APPENDIX XV
co2water = 0.59;
co2energy = 600;
co2detergent = 2;
LOADamoountTOTAL = PERSON * WochenLA;
WMRECOMENDEDload30 = WMV*LB30;
WMRECOMENDEDload40 = WMV*LB40;
WMRECOMENDEDload60 = WMV*LB60;
WOCHENLA30 = round(LOADamoountTOTAL * Amountof30);
WOCHENLA40 = round(LOADamoountTOTAL * Amountof40);
WOCHENLA60 = round(LOADamoountTOTAL * Amountof60);
WochenCounterGENERAL = 0
m=0;
WASCHKORB= 0;
WASCHKORB30 = 0;
RESTLOAD =0;
TEMP=30;
MWD = MWD30;
WochenCounterREG30 = 0;
WochenCounterNOT30 = 0;
WieoftgewaschenREG30 = 0;
WieoftgewaschenNOT30 = 0;
NOTWASCHGANG = 0;
REG1ODERNOT2 = 0;
DETwaschwoche =0;
CWmwwaschwoche =0;
CEmwwaschwoche =0;
CO2DETwaschwoche = 0;
CO2CWmwwaschwoche =0;
CO2CEmwwaschwoche =0;
CEmwwaschwocheSCHLEIFE=0;
DETwaschwocheSCHLEIFE =0;
CWmwwaschwocheSCHLEIFE = 0;
vektorWASCHKORB1 = zeros (1,17);
for n=1:(DOS);
REG1ODERNOT2 = 3;
WochenCounterGENERAL = WochenCounterGENERAL+1;
Waschkorb30 = WOCHENLA30 + RESTLOAD;
if Waschkorb30 < WMRECOMENDEDload30 && WochenCounterNOT30 <
MAXIMALEWARTEZEITWASCHEN
RESTLOAD = Waschkorb30;
WochenCounterNOT30 = WochenCounterNOT30 +1;
elseif Waschkorb30 < WMRECOMENDEDload30 &&
WochenCounterNOT30 == MAXIMALEWARTEZEITWASCHEN
m=m+1;
WASCHKORB = Waschkorb30;
REG1ODERNOT2 = 2;
WOCHENLA = WOCHENLA30;
APPENDIX XVI
[DET, CWmw, CEmw, vektorWASCHKORB] = Waschmaschine(BETA,
WP, TEMP, WMV, MWD, WASCHKORB, m, WochenCounterGENERAL,
RESTLOAD, REG1ODERNOT2, PERSON, LOADamoountTOTAL,
WOCHENLA,n,SZX);
vektorWASCHKORB = vertcat(vektorWASCHKORB1,
vektorWASCHKORB);
vektorWASCHKORB1=vektorWASCHKORB;
WochenCounterNOT30 = 0;
NOTWASCHGANG = NOTWASCHGANG+1; % Anzahl der
NOTWaschgägnge
RESTLOAD =0;
REG1ODERNOT2 = 0;
end
while Waschkorb30 >= WMRECOMENDEDload30 %Reguläres Waschen
m=m+1;
RESTLOAD = Waschkorb30 - WMRECOMENDEDload30;
WASCHKORB = WMRECOMENDEDload30;
REG1ODERNOT2 = 1;
WOCHENLA = WOCHENLA30;
[DET,CWmw,CEmw, vektorWASCHKORB] = Waschmaschine(BETA,
WP, TEMP, WMV, MWD, WASCHKORB, m, WochenCounterGENERAL,
RESTLOAD, REG1ODERNOT2, PERSON, LOADamoountTOTAL, WOCHENLA,n,
SZX);
vektorWASCHKORB = vertcat(vektorWASCHKORB1,
vektorWASCHKORB); %
vektorWASCHKORB1=vektorWASCHKORB;
WochenCounterREG30 = WochenCounterREG30 +1;
Waschkorb30=RESTLOAD;
WochenCounterNOT30 =0;
REG1ODERNOT2 = 0;
end
vNOTWASCHGANG(n+1,1) =NOTWASCHGANG;
vWochenCounterGENERAL (n+1,1) = WochenCounterGENERAL;
if REG1ODERNOT2 == 3;
DET = 0;
CWmw =0;
CEmw =0;
REG1ODERNOT2=3;
WASCHKORB=0;
WOCHENLA =0;
vektorWASCHKORB=zeros(1,17); %
vektorWASCHKORB (1,:) = [n, m, WochenCounterGENERAL,
PERSON, LOADamoountTOTAL, WOCHENLA, WASCHKORB, TEMP,WMV,MWD,
RESTLOAD, WP, DET, CWmw, CEmw, REG1ODERNOT2, SZX];
vektorWASCHKORB2 = vertcat(vektorWASCHKORB1,
vektorWASCHKORB);
vektorWASCHKORB1=vektorWASCHKORB2;
end
APPENDIX XVII
end
TEST30 = vektorWASCHKORB1;
vektorWASCHKORB1=zeros(1,17);
ACKNOWLEDGEMENTS
Acknowledgements
First of all I would like to express my thanks to Prof. Dr. Rainer Stamminger who gave
me this exciting topic. His interest in my work, qualified support, swift feedback and
many helpful discussions as well as the technical and editorial advices were an
important prerequisite for the successful completion of this thesis.
I also would like to thank Prof. Dr. Michael-Burkhard Piorkowsky who agreed to
become the second examiner.
Furthermore, I would like to thank to Henkel KGaA who made this work possible.
Especially, I want to thank to Dr. Christian Nitsch and Mr. Arnd Kessler for their
support and the readiness for discussions.
I also would like to thank the team of the Section of Appliance Technology at
University of Bonn. Especially I would like to thank Marina Niestrath and Stefan Dodel
who conducted the washing machines tests. Furthermore I would like to thank to Dr.
Gereon Broil for the technical assistance and to Maria Braun, Edith Lambert, Ina Hook
and Yvonne Drechsler for their help.
I would like to thank all my friends, especially to Maria Braun, Rico Baumgartl and Jan
Henning Eggert. You always believed in me and made sure that I never felt alone.
Last but not least I will forever be thankful to my family, especially my parents Mirsada
and Esad as well as my brother Admir for their never-ending support in my life.
ACKNOWLEDGEMENTS
CURRICULUM VITAE
Curriculum vitae
Emir Lasic
Date of birth: December 4th
, 1979
Sanski Most, Bosnia and Herzegovina
July 1998 Matura in Sarajevo, Bosnia and Herzegovina
2002 - 2005 Study of food technology science, University of Bonn
2006 - 2009 Study of nutrition and home economics science, University of Bonn
2009 Diploma Thesis: ”Akzeptanz von Haushaltsrobotern am Beispiel von
Care-o-bot 3”
2009 -2014 Ph.D. student at “Household and Appliance Technology Section” of the
“Institute of Agricultural Engineering” of the University of Bonn